The influence of mineral admixtures on the rheology of cement paste and concrete

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再生混凝土耐久性影响因素分析

再生混凝土耐久性影响因素分析

再生混凝土耐久性影响因素分析蒙秋江;应敬伟【摘要】通过总结再生混凝土耐久性的影响因素,得出了不同因素对再生混凝土耐久性的影响特征。

在相同配合比和再生骨料品质的情况下,混凝土的耐久性随着再生骨料取代率的增加而降低,但随着龄期的增加而增强;再生骨料中所含有的湿度对新拌混凝土的耐久性的影响是明显的,RAC抵抗周期荷载循环的能力随着水饱和度的增加而变大;对于潮湿养护条件,再生骨料对混凝土渗透性的影响并不明显。

%According ot the summary of the influencing factors of the recycled concrete’s durability,the paper concludes the influence features of the various factors on the durability,indicates the concrete durability lowers along with the increasing the replacing ratio of recycled aggregate under the same mix proportion and quality of the recycled aggregate,but it turns to be better with increasing ages,illustrates the humidity in the recycled aggregate has the evident influence on the newly-mixed concrete durability,while the RAC capacity to resist the period loading circle, and proves the recycled aggregate has unclear influence on concrete’s permeability under the moist maintenance.【期刊名称】《山西建筑》【年(卷),期】2015(000)016【总页数】2页(P104-105)【关键词】再生混凝土;取代率;龄期;湿度【作者】蒙秋江;应敬伟【作者单位】广西大学土木建筑工程学院,广西南宁 530004;广西大学土木建筑工程学院,广西南宁 530004; 广西理工科学实验中心,广西南宁 530004【正文语种】中文【中图分类】TU528再生混凝土的质量受到许多因素的影响,其影响因素如图1所示。

节约矿产资源的英语作文

节约矿产资源的英语作文

节约矿产资源的英语作文Mining resources are a precious and limited natural asset for our planet. It's crucial that we conserve them carefully to ensure sustainable development for future generations.Everyday activities, like driving cars and building homes, rely heavily on minerals extracted from the earth. But mining these resources can have a significant impact on the environment, causing land degradation and water pollution. So, it's essential to use them sparingly and efficiently.One way to conserve minerals is by recycling. Many products made from metals can be reused or repurposed, reducing the need for new mining. Simple habits likesorting our waste and using recycled materials can make a big difference.Another approach is to adopt alternative technologies.For instance, renewable energy sources like solar and wind power can help reduce our dependence on fossil fuels, which require a lot of mining for extraction.Lastly, it's important to raise awareness about the importance of mineral conservation. Educating people about the environmental impact of mining and the benefits of conservation can help create a more sustainable society.In conclusion, conserving mineral resources is vitalfor our planet's future. By recycling, adopting alternative technologies, and spreading awareness, we can allcontribute to this important effort.。

混凝土抗碳化性能综述

混凝土抗碳化性能综述

混凝土抗碳化性能综述摘要:混凝土的抗碳化性能作为影响其耐久性的重要因素之一,对于混凝土结构的可持续性发展具有十分重要的意义。

本文介绍了混凝土的碳化影响因素、碳化机理及相关模型,展望了大产量矿物掺合料混凝土抗碳化性能的发展及方向。

关键词:混凝土,碳化,大掺量矿物掺合料混凝土1、绪论混凝土作为一种重要的建筑材料,其质量优劣直接关系到建筑整体质量。

在混凝土长期使用过程中,由于人们对其耐久性问题认识不够深入,严重影响其安全使用,而其中,一个重要的问题就是混凝土的碳化,这是关系到混凝土耐久性的经典问题,经过大量研究和实践,许多具有潜在化学活性的矿物掺合料(粉煤灰、磨细矿渣等)逐渐步入人们视野。

研究发现,对于粉煤灰混凝土,粉煤灰掺量增大时混凝土抗碳化能力会降低,当粉煤灰掺量不超过40%时,混凝土抗碳化能力基本满足,但当其掺量大于50 %后,混凝土碳化速率将明显提高。

另对于矿渣混凝土其抗碳化性能要弱于普通混凝土,当选用的矿渣粉比表面积在600 m2/kg以上时,其抗碳化能力相对较好。

同时,对双掺粉煤灰、矿渣与粉煤灰、硅灰的混凝土的抗碳化性能进行了研究发现掺入硅灰后,其抗碳化性能增强。

一般来说,矿物掺合料的二次水化反应会使混凝土浆体碱度会更低,使混凝土的抗碳化性能远低于纯硅酸盐水泥混凝土,不利于其广泛应用。

如何处理好该问题,对于混凝土结构的可持续性发展具有十分重要的意义。

2、矿物掺合料混凝土的抗碳化性能研究2.1 混凝土碳化影响因素研究混凝土碳化同诸多因素相关,这些影响因素基本可以以内部因素和外部因素来进行区分。

2.1.1 混凝土内部因素的影响(1)水泥品种及用量水泥对CO2的吸收速率随其品种的不同而存在差异,水泥用量一定的前提下,混凝土的抗碳化性能:粉煤灰混凝土>普通硅酸盐水泥混凝土>硅酸盐水泥混凝土[。

许丽萍等研究了水泥品种对混凝土碳化速率的影响,试验结果如表1所示,另外,不同水泥用量对混凝土碳化深度的影响如表2所示。

热点14 自然资源利用与生态修复---备战2021年高考英语考前时事热点话题阅读+题型专练

热点14 自然资源利用与生态修复---备战2021年高考英语考前时事热点话题阅读+题型专练

备战2021年高考英语考前时事热点话题阅读热点14 自然资源利用与生态修复一、阅读理解1In a world with limited land, water and other natural resources, the harm from the traditional business model is on the rise. Actually, the past decade has seen more and more forests disappearing and the globe becoming increasingly warm. People now realize that this unhealthy situation must be changed, and that we must be able to develop in sustainable(可持续的)ways. That means growth with low carbon or development of sustainable products. In other words, we should keep the earth healthy while using its supply of natural resources.Today, sustainable development is a proper trend in many countries. According to a recent study, the global market for low-carbon energy will become three times bigger over the next decade. China, for example, has set its mind on leading that market, hoping to seize chances in the new round of the global energy revolution. It is now trying hard to make full use of wind and solar energy, and is spending a huge amount of money making electric cars and high-speed trains. In addition, we are also seeing great growth in the global markets for sustainable products such as palm oil(棕榈油), which is produced without cutting down valuable rainforest. In recent years the markets for sustainable products have grown by more than 50%.Governments can fully develop the potential of these new markets. First, they can set high targets for reducing carbon emissions and targets for saving and reusing energy. Besides, stronger arrangement of public resources like forests can also help to speed up the development. Finally, governments can avoid the huge expenses that are taking us in the wrong direction, and redirecting some of those expenses can accelerate the change from traditional model to a sustainable one.The major challenge of this century is to find ways to meet the needs of growing population within the limits of this single planet. That is no small task, but it offers abundant new chances for sustainable product industries.1. The traditional business model is harmful because of all the following EXCEPT that ______.A. it makes the world warmerB. it consumes natural resourcesC. it makes growth hard to continueD. it brings severe damage to forests2. To fully develop the low-carbon markets, governments can ______.A. cut public expensesB. forbid carbon emissionC. develop public resourcesD. encourage energy conservation3. We can learn from the last paragraph that businesses have many chances to ______.A. develop sustainable productsB. explore new natural resourcesC. make full use of natural resourcesD. deal with the major challenge4. What is the main purpose of the passage?A. To compare two business models.B. To introduce a new business model.C. To advocate sustainable development.D. To predict a change of the global markets.2A rainforest is an area covered by tall trees with the total high rainfall spreading(扩大)quite equally through the year and the temperature rarely falling below 16°C. Rainforests have a great influence on the world environment because they can take in heat from the sun and adjust the climate.Without the forest cover, these areas would reflect(反射)more heat into the atmosphere, warming the rest of the world. Losing the rainforests may also influence wind and rainfall patterns,potentially(潜在地)causing certain natural disasters all over the world.In the past hundred years, humans have begun destroying rainforests in search of three major resources :land for crops, wood for paper and other products, land for raising farm animals. This action affects the environment as a whole. For example, a lot of carbon dioxide in the air comes from burning the rainforests. People obviously have a need for the resources we gain from cutting trees but we will suffer much more than we will benefit.There are two main reasons for this. Firstly, when people cut down trees, generally they can only use the land for a year or two. Secondly, cutting large sections of rainforests may provide a good supply of wood right now, but in the long run it a ctually reduces the world’s wood supply. Rainforests are often called the world's drugstore. More than 25% of the medicines we use today come from plants in rainforests. However, fewer than 1% of rainforest plants have been examined for their medical value. It is extremely likely that our best chance to cure diseases lies somewhere in the world’s shrinking(减少)rainforests.5. Rainforests can help to adjust the climate because they______.A. reflect more heat into the atmosphereB. bring about high rainfall throughout the worldC. rarely cause the temperature to drop lower than 16°CD. absorb(吸收)the heat from the sun, reducing the effect of heat from the sun on the earth6. What does the underlined word “this” in the third paragraph refer to?A. We will lose much more than we can gain.B. Humans have begun destroying rainforests.C. People have a strong desire for resources.D. Much carbon dioxide (二氧化碳)comes from burning rainforests.7. It can be inferred from the text that______.A. we can get enough resources without rainforestsB. there is great medicine potential in rainforestsC. we will grow fewer kinds of crops in the gained landD. the level of annual rainfall affects wind patterns8. What might be the best title for the text?A. How to Save Rainforests?B. How to Protect Nature?C. Rainforests and the Environment.D. Rainforests and Medical Development.3Ohio—Lake Erie, the smallest of North America's five Great Lakes, supplies fresh drinking water to an estimated 11 million people in Ohio, Michigan and southern Ontario province, Canada.Yet sometimes pollution, bath from industrial waste and farm-chemical run-off, leaves large areas of the lake covered in half-meter-thick layers of green slime. Scientists blame a lot of chemicals entering the water, which has caused pollution.To find out where these extra nutrients come from, the Ohio Department of Natural Resources has been studying data from its network of 14 water-quality monitoring stations installed along the rivers that flow into the Lake Erie basin.At one point, water from the small stream is diverted into a pipe where it is pumped into the testing station.We'll have 'a sample a day, year-round every day so that really pins down what the chemistry is like," says Dave Baker of Ohio's Heidelberg University, who takes charge of the monitoring stations for the Department of Natural Resources.The U.S. Environmental Protection Agency, the federal government's pollution watchdog, requires pointsources, such as factories, to monitor and report their discharges. So Baker is looking for where the other sources of pollution come from."If there are problems in Lake Erie, we want to know where it's coming from and make sure we're putting resources to solve the problem properly," Baker says.In this case, a primary source of the pollution turns out to be chemical fertilizer that turn off farmland during rainstorms.Because farmers believe fertilizers are essential to high crop yields, they would like to use them. However, the USDA's Natural Resource Conservation Service isn't asking them to abandon farm chemicals, but rather to use them more sparingly so they don't run off the land when it rains.Another technique for reducing farm chemical pollution of Lake Erie is cover-crop farming. After the harvest, farmers plant a second quick-growing crop to reduce erosion. The deep-rooted plants, such as rye or turnips, help to cover the soil, allowing worms and fungi to work their magic and helping the soil to absorb more water and nutrients.9. What is the problem with Lake Erie?A. There are no fish in it.B. There is little water in it.C. The water is unfit to drink.D. It contains a lot of chemicals.10. Who provides data about Lake Erie?A. The water-quality monitoring stations.B. Natural Resource Conservation Service.C. The Ohio Department of Natural Resources.D. The U.S. Environmental Protection Agency.11. The underlined phrase "pins down" in Paragraph 5 probably means " ".A. looks throughB. explains exactlyC. keeps a record ofD. shows clearly12. What causes the pollution in Lake Erie?A. Animal waste from nearby farms.B. Waste water from a nearby factory.C. Chemical fertilizers from the fields.D. Pesticide farmers used to kill locusts.13. Quick-growing crops can be planted to .A. prevent worms from eating cropsB. increase the harvest of the farmersC. make full use of chemical fertilizers in the soilD. keep the soil from being washed away4Hidden away in the mountains of western Tanzania is one of the largest lakes in the world: Lake Tanganyika.Environmentalists want to protect the beauty and biological diversity of this area from the harmful effects of overfishing and deforestation. However, in order to do this, they need the cooperation of people in the nearby village of Mahale. In this poor community, malaria and typhoid (疟疾和伤寒) are spreading, there is little access to doctors and 13% of children die before age 5. How can we expect people who cannot save their own children to care about saving the environment?While it is true that the Mahale villagers are suffering, environmentalists argue that Lake Tanganyika is in an equally terrible condition. This lake is home to hundreds of fish species found nowhere else on the globe. Eighty mammal species live in the surrounding forests and mountains. 90% of Tanzania’s endangered chimpanzees live in this area. Damage to this ecosystem will result in untold losses. Furthermore, environmentalists see the destruction of the environment as a direct function of the villagers’ poverty (贫穷): as the fish population decreases, people are forced to clear more land to grow rice and corn. As they clear more land, the soil run-off from deforestation further reduces the fish population, making it even more difficult for people to survive on fishing alone. This cycle harms both the Mahale villagers and the environment.To meet their goal of protecting Lake Tanganyika, environmentalists are now using a many-sided approach in Mahale: helping the villagers gain access to healthcare, educating fishermen and farmers about the effect of deforestation and their own role in the decreasing fish population, and protecting areas of the lake where fish lay eggs. Since natural resources can be the tool by which the people of Tanzania work themselves out of poverty, it is essential that these resources are managed well. By combining health services with protection activity, we can begin to heal the suffering in western Tanzania, for people and the land alike.14. What do we know about Lake Tanganyika from the passage?A. It leads to the people’s poverty.B. It faces a serious situation now.C. It is the largest lake in the world.D. It’s home to some unique animals in the world.15. Which of the following might environmentalists agree with?A. Saving lives is more important than saving the lake.B. Offering the locals healthcare directly contributes to less fishing of the lake.C. Educating the locals can promote their awareness of environmental protection.D. Gaining access to natural resources is the only way for locals to fight poverty.16. What might be the best title for the passage?A. Protecting Lake TanganyikaB. The Poor Life of Villagers in MahaleC. The Importance of Lake TanganyikaD. Villagers in Mahale and Lake Tanganyika5In the oceans, concrete is the main construction material, accounting for more than 70% of coastal and marine construction such as ports, coastal defence structures and waterfronts. "Concrete is damaging in the ocean because, to put it in place, natural ecosystems are destroyed," says Alex Rogers, director of science at REV Ocean, a not-for-profit company studying ocean health and raising awareness of global impacts on the marine environment. "Concrete is a conventional material, and it is low cost. But really, in this day and age, we should be looking at alternative materials that have a lower impact on the environment."Those alternatives might already be here. Among them is a substance called ECOncrete, developed as an eco-friendly concrete. ECOncrete produces bio enhancing concrete products intended to protect coastlines and marine resources. This is achieved by using a mixture made almost entirely of by-products and recycled materials, and is thus nearly carbon neutral. This mixture is combined with up to 70% slag cement(a by product of the steel industry which has a low carbon footprint) and is beneficial for marine concrete thanks to its high chloride resistance. The overall result is a low-carbon concrete.Furthermore, unlike traditional concrete, which is highly alkaline, the specially designed concrete has a pH value near to that of sea water, which helps to promote the growth of marine species such as crabs, molluscs, clams, mussels and oysters. ECOncrete's products are already in use across eight countries and six different seas, from seawalls in Hong Kong to the Port of Rotterdam.However, Beth Strain, a lecturer in marine biology and a project leader for Australia's National Centre for Coasts and Climate, says the evidence for eco-friendly concrete as a better surface for marine organisms is very mixed. “It can be location specific. We did an experiment in 15 harbours around the world with the same type of concrete surface complexity. Largely, the results were positive, but in Penang, Malaysia, for example, using eco-friendly concrete that would theoretically retain moisture and be better for organisms to survive on made no difference.” Strain thinks this is because of th e area's typhoons, which make the area very wet already, so the features of the concrete aren't a big help.“There is a degree of difference and each location will have its own environmental challenges,” says Strain.Nevertheless, from multiple perspectives, it appears that nature-based solutions are definitely the way forward.17. What can we know about ECOncrete from paragraph 2 and 3?A. It is a substance that is highly alkaline.B. It is a substance made of eco-friendly materials.C. It is a company aiming to keep marine resources safe.D. It is a mixture which is combined with low-carbon concrete.18. What does Beth Strain's attitude towards eco-friendly concrete?A. Negative.B. Indifferent.C. Objective.D. Supportive.19. What caused the result in Penang according to Beth Strain?A. The climate of the area.B. The pH value of sea water.C. The researchers of the project.D. The diversity of marine organism.20. Which one may be a possible solutions in the future?A. Invent a new artificial material.B. Install monitors under the oceans.C. Pull down all the coastal constructions.D. Use eco-blocks in coastal constructions.6"We are running out of space and the only places to go to are other worlds. ... Spreading out may be the only thing that saves us from ourselves. I am convinced that humans need to leave Earth" These are the words of the famous scientist Stephen Hawking.Hawking was not alone in this view. Many experts feel that the only way for humans to last far into the future is to colonize (殖民) other planets. That way, if an asteroid (小行星), a terrible discase, or some other disaster strikes Earth, we would still have a chance. Mars is one of the best choices. NASA, the private company SpaceX,and other organizations all have plans to send humans there. "Either we spread Earth to other planets, or we go out of existence,” SpaceX founder Elon Musk said.But not everyone agrees that colonizing Mars or any other planet is such a great plan. The most common argument against going is that it's just too expensive or dangerous. It will take huge amounts of money and other resources just to get people there, let alone set up a place for them to live. It's not even clear if humans could survive on Mars.Maybe all the time and money people would pour into a Mars task would be better spent on more importantprojects here on Earth, like dealing with poverty or climate change. Some experts argue that handling a problem like an asteroid strike or disease outbreak while staying here on Earth would be much easier and less expensive than surviving on a new planet. In addition, moving to a new planet could harm or destroy anything that already lives there. Mars seems uninhabited, but it could possibly host some life. Human visitors may destroy this life or change the Martian environment forever. What do you think? Should humans colonize outer space or stay at home?21. In writing Paragraph 1, the author aims to________A. provide an explanationB. make a comparisonC. reach a conclusionD. introduce a topic22. In Paragraph 2, many experts recommend colonizing Mars in order to ________.A. protect humans from dying outB. make Hawking's dream come trueC. seek more space for humans to live inD. encourage different organizations to compete23. For what reason are some scientists against colonizing Mars?A. Out of space, out of mind.B. Money should be well spent.C. East or west, home is the best.D. One should mind his own business.24. What’s the author's attitude towards colonizing Mars?A. Confident.B. Doubtful.C. Objective.D. Supportive.7In Australia and other developed countries, consumption (消耗) is viewed as important for economic growth. In recent years, however, concern has grown about the increasing number of people consuming limited resources at a shocking rate. The United States has only about 5 percent of the world's population, yet consumes about 35 percent of the world's energy.Impressive packaging and storage such as refrigeration is a luxury (奢侈) that consumers in developed countries take for granted (认为理所当然). In many parts of the world where refrigeration is either unavailable or too expensive, fresh food is bought daily from open-air markets.These markets make little influence on the environment. They do not use energy to store food and because they mostly operate during daylight hours, no electricity is used for lighting. Packaging is mostly unnecessary, and when needed, is often made from biodegradable (可生物降解的) vegetable matter. These markets still exist inmany parts of the developed world, but are an alternative (供选择的) form of shopping. Even in developing countries, shops are fast becoming the main places for consumers.Commercial (商业的) packaging is becoming as much a part of consumption in developing countries as it is in developed countries. Plastic bags, drink cans, and hamburger containers are now thrown into rubbish piles along with banana leaves which are a more traditional form of packaging. In most cases, it all ends up at the local garbage disposal plant and is not recycled.Many people are starting to notice the influence of consumerism on the environment. It is affecting not only the earth, but also our health. Some scientists think that the greenhouse effect has increased due to the production, use and disposal of many of the products we use.25. What does the author think of packaging and refrigeration?A. It's quite necessary.B. It's a costly process.C. It's the progress of society.D. It's different from consumerism.26. What can be known about the open-air markets in developing countries?A. They are not changing.B. They can't be seen now.C. They are getting less popular.D. They are appearing in more places.27. What are rarely used as packaging according to the author?A. Drink cans.B. Plastic bags.C. Banana leaves.D. Hamburger containers.28. What's the best title for the text?A. Different Ways of PackagingB. Technology vs. the EnvironmentC. Markets in Developing CountriesD. Consumption vs. Economic Growth8A group of scientists are hurrying to document and protect the ancient ruins along Puerto Rico's coasts. They are working as fast as they can before rising sea levels destroy a large part of the island's history.The work started in August 2017. With the help of 3D imaging and other advanced technologies, the scientists have explored a large piece of land along Puerto Rico's north coast and identified an ancient ceremonial center used by the Taino Indians. About 2,000 years ago, the Tainoes lived on many islands in the Caribbean Sea. But after the arrival of Christopher Columbus and other Europeans, they were all killed.Scientists also found a large living place just east of the site? which is seriously endangered by rising sea levels and other natural disasters. Puerto Rico's Department of Natural Resources has said the sea level around the island is rising by more than 3 mm every year.However, climate change has more immediate effects. These include the destruction of the Puerto Rico coastline and natural habitats by storms.Warmer temperatures in the Caribbean increase the number and strength of storms and Puerto Rico faces the possibility of storms every year for six months during the Atlantic hurricane season. Hurricane Maria had already washed away part of its history.Scientists are now trying to find out how badly the hurricanes and loss of land have affected the heritage site they are studying. Eric Lo is an engineer who flew to Puerto Rico in August 2017 to start the project one month before Maria struck the island. Lo was surprised at what he saw when he returned months later.“Pieces of land where I stood do not exist anymore. They are underwater,” he said.29. Where did the scientists find the ancient Taino Indians' living place?A. Under the Caribbean Sea.B. In a European country.C. On Puerto Rico's north coast.D. Along Puerto Rico's east coast.30. Why have the Tainos disappeared from the islands in the Caribbean Sea?A. They were killed by the Europeans.B. They were destroyed by Hurricane Maria.C. They were driven away by the rising sea levels.D. They were moved away by their government.31. What is paragraph 5 mainly about?A. The serious damage caused by storms.B. The plan to protect the heritage sites.C. The loss of natural habitats in Puerto Rico.D. The worsening climate conditions in the world.32. Which of the following can be the best title for the text?A. The Obvious Effects of Global Climate ChangeB. Efforts to Preserve Puerto Rico's Coastal HeritageC. New Discoveries of Ancient Taino Indians' RuinsD. Technologies Used to Identify the Ancient Ruins9This season, the bushfires in Australia have burned more than 12.35 million acres of land. At least 25 people have been killed and 2000 homes destroyed. According to the BBC, this is the most casualties (伤亡) from wildfires in the country since 2009. The University of Sydney estimates that 480 million animals have died in South Wales alone.Zeke Hausfather, an energy systems analyst and climate researcher at Berkeley Earth, said warmer temperatures and extreme weather have made Australia more susceptible to fires and increased the length of the fire season. “The drier conditions combined with record high temperatures in 2019 created main condition s for the disastrous fires. Australia’s fires were worsened by the combination of those two. 2019 was the perfect storm for being the warmest year on record for Australia and the driest year on record for Australia,” Hausfather added on Friday.Kevin Trenberth, a senior scientist at the US National Center for Atmospheric Research, said warmer ocean temperatures also contributed to more variable weather around the world. Trenberth believes that global warming contributed to energy imbalances and hot spots in the oceans, which can create a wave in the atmosphere that locks weather patterns in places, causing longer rain events in Indonesia, for example, and at the same time contributing to drought in Australia. He said that once an area experiences drought conditions for two months or more, it increases the risk of fires catching and spreading. Those changing weather patterns due to global warming make drought events longer.Climate experts stress that climate change is not the only factor in the severity of wildfires. How land is managed can also impact the amount of fuel available for fires. Practices like controlled burns and other factors can impact the risk to people and property, such as warning systems and the type of development in a given area. Changing those policies has great potential to limit future damage from wildfires along with changes to how firemanagement resources are dispatched (派遣).33. What are the numbers about in Paragraph 1?A. The causes of Australian fires.B. The results of Australian fires.C. The damaged areas of Australian fires.D. The property destruction of Australian fires.34. Which of the following best explains “susceptible to” in the second paragraph?A. Very quickly to adapt to.B. Very seriously to focus on.C. Very easily to be protected against.D. Very likely to be influenced by.35. What can we infer from Trenberth’s research?A. Warmer ocean temperatures promote fires spreading.B. Longer dry weather contributes to global warming.C. The imbalanced energy leads to the temperature rising.D. Global warming is the root cause of the bushfires.36. What does the author intend to do in the last paragraph?A. To provide some advice about reducing damage.B. To show the methods for controlling burns.C. To predict the seriousness of Australian fires.D. To stress the effects of Australian fires.10The best and most-commonly used sources for the pills we have are oily fish like salmon(畦),mackerel and sardines. Many environmentalists fear that some species are being over fished for this purpose. We may have an endless voracity for fish oil, but we don't have an endless supply of fish.Menhaden, which is described as “a big-headed, smelly, foot-long fish" , is in great danger. Although prized for dinner in the 18th century, the species has become the unknown victim of the fish oil business 9 which presents us with potential sea fish. Menhaden filter-feed almost entirely on algae (海藻)and is especially good at changing it into-3 fatty acids, which make them a good target for fish oil companies.One particular company, Protein of Houston, has been fishing 90 percent of the country' s menhaden. It's become such a big problem that 13 of the 15 Atlantic states have banned the company * s boats from their waters. Yet the company is still allowed to fish in North Carolina and Virginia, as well as federal waters; the company * s efforts result in the removing of half a billion menhaden every year.Aside from running out a public natural resource for a company,s private profit, the damage to the ecosystem is cause for alarm. The muddy brown color of the Long Island Sound is the direct result of lacking water nitration (过滤)一a job that was once done by menhaden.Menhaden keep the ocean waters of the Atlantic and Gulf coasts clean. A menhaden filters four to six gallons of water of algae in a minute, which prevents underwater dead zones.Measures should be taken to avoid the over fished situation. Plant seeds such as flax seed, chiaseeds, hemp seeds, and sesame seeds —and particularly their oils —are good vegetarian sources of omega-3 fatty acids, although the mix of specific acids is different from which one can get with fish.37. Why does menhaden become a good fish for companies to make pills?A. It is good at forming-3 fatty acids.B. It feeds mainly on the harmful algae.C. It is well-known for its rich protein.D. It is relatively easy for companies to catch.38. What does the underlined word "voracity" in paragraph 1 mean?A. troubleB. shortageC. resourceD. appetite39. What does the author intend to suggest us in the last paragraph?A. To grow more plants for their seeds to make oil.B. To use some substitutes instead of more fish oil.C. To call on the government to make laws in fishing.D. To take part in more activities to protect the environment.40. What is the best title for the text?A. The broken natural ecosystem.B. The process of making fish oil.C. Bad effects of fish oil making.D. How to use natural resources.11Henderson Island in the South Pacific Ocean has always been known for its remarkable biological diversity and untouched ecology. Now, the remote UNESCO World Heritage site that lies 3,100 miles from the closest human settlement can also lay claim to being one of the most polluted places on Earth.Jennifer Lavers, a researcher from the University of Tasmania’s Institute for Marine and Antarctic Studies who。

211262186_Cu-MOF_材料的合成及其对有机小分子的荧光识别

211262186_Cu-MOF_材料的合成及其对有机小分子的荧光识别

第52卷第5期 辽 宁 化 工 Vol.52,No. 5 2023年5月 Liaoning Chemical Industry May,2023基金项目:① 2021年贵州省大学生创新创业训练计划项目(国家级)(项目编号:202110667029) ;②2021年贵州省大学生创新创业训练计划 项目(省级)(项目编号:202110667005);③贵州省教育厅2021年度市(州)普通本科高校青年科技人才成长项目(项目编号:黔 教合KY 字[2022]036号)。

收稿日期: 2022-09-29Cu -MOF 材料的合成 及其对有机小分子的荧光识别文勇武,江创,张玉蝶,熊琴,赵永婷*(安顺学院, 贵州 安顺 561000)摘 要:通过水热法合成了一例Cu-MOF 材料(化合物1)。

单晶衍射分析表明化合物1属于单斜晶系,空间群为P21/c ,晶胞参数a = 7.309 6,b =10.917 4,c =14.114 5,α=90,β=91.497,γ=90 。

对化合物1进行荧光性能研究,荧光结果分析表明,在260 nm 的激发波长下,化合物1在390 nm 处有强的荧光发射峰。

并研究了化合物1对不同有机溶剂分子的荧光特性。

通过荧光光谱测试表明,化合物1在乙醇溶液中表现出荧光猝灭现象,对乙醇溶剂具有良好的荧光识别性能。

关 键 词:Cu-MOF 材料;有机溶剂;荧光;识别中图分类号:TQ201 文献标识码: A 文章编号: 1004-0935(2023)05-0627-04金属有机框架材料(MOFs ),又称为配位聚合物材料,是由金属离子或者金属团簇与有机配体通过配位键自组装连接而成的一维、二维或三维结 构[1]。

金属中心的配位模式、金属半径大小以及配体的配位齿的数目、配位点间的间距、配体的给体基团性质等都会对整个自组装过程起决定性作用。

合成MOFs 材料的方法主要有水热法、溶剂热法、微波合成法、电化学法和其他方法等[2-4],水热合成至今已有100多年历史,目前已经发展成金属有机框架材料合成的主要途径之一。

Theimpactofminer...

Theimpactofminer...

IntroductionThe availability of plant nutrients in sufficient quantities and their correct balance is a prerequisite for plant growth and hence yield. The use of mineral fertilizer as a source of plant nutrients is essential for sustainable agriculture. Mineral fertilizers are applied to balance the gap between the permanent export of nutrients from the field with the harvested crops and the nutrients supplied by the soil and by available organic sources (see Fig. 1).Figure organic sources and the nutrient demand for optimum crop developmentAn increasing world population will demand increasing food production (FAO, 2006) that needs to be produced from a limited agricultural area (FAO, 2003). As a consequence the agricultural productivity in terms of yield per hectare has to be improved to sustain sufficient global supply of food, feed and bio-energy. Intensive crop production with economically optimum fertilizer input is an option to support this development because it allows utilizing the yield potential of agricultural crops.As all human activities also intensive crop production and in particular the use of mineral fertilizer has an “environmental footprint”. With regards to N fertilizers this is mainly related to eutrophication and acidification of natural and semi-natural ecosystems, and the release of greenhouse gases (GHG). This paper investigates the GHG emissions (“carbon footprint”) of crop production in general and the intensity of mineral N fertilizer use in particular.Climate change – the contribution of agriculture in general and of mineral fertilizer in particularFigure 2 shows the contribution of different sectors to the global GHG emissions in 2004 (IPCC, 2007; Bellarby, 2008). According to IPCC (2007), agricultural GHG emissions include: •Methane (CH4) emissions from enteric fermentation (cattle farming)•CH4 from rice cultivation•Nitrous oxide (N2O) from application of organic and mineral N sources•N2O and CH4 from manure handling (storage etc.), and•N2O and CH4 from burning of crop residues etc.Mineral fertilizers are mainly involved in N2O emissions from soils. According to Bellarby et al. (2008) agricultural soils emit 2128 Tg CO2-equivalents (CO2eq) as N2O. In order to distinguish between N2O from mineral fertilizer application and N2O from organic N sources theIPCC estimation methodology (IPCC, 2006) was applied. A global consumption of 90 Tg mineral N (IFA statistics for 2004/2005) gives combined direct and indirect N2O emission from mineral fertilizer application of 561 Tg CO2eq, which is 1.2% of the total global GHG budget or 26% of the N2O emissions from agricultural soils. The remaining 1567 Tg CO2eq have to be allocated to organic N sources such as manure, crop residues and sewage sludge.Agricultural GHG emissions according to IPCC (2007) have a share of 13.5% in the total GHG emission. There are also GHG emissions assigned to other sectors than agriculture that are directly linked to agricultural production. The production of N fertilizer releases 410 Tg CO2eq per year, which is equivalent to 0.8% of the global GHG emissions. The loss of carbon due to land use change from natural area (mainly forest) into agricultural land contributes on average about 12% (uncertainty range of 6 - 17%) to the global GHG emissions (Bellarby et al., 2008). In total all GHG emissions related to agriculture amount on average to 26% of the total global GHG emissions with a range between 17 and 32% because of the uncertainty of the land use data.Total GHG emission related to agriculture: 26% (17-32%)Figure 2:Contribution of all activities related to agriculture to the global GHG emissions in 2004 (IPCC, 2007; Bellarby et al., 2008; * own calculations)These data show that the production and use of mineral and organic N fertilizer contributes significantly to the global GHG budget, but the major contribution related to agriculture is the expansion of agricultural land into forests and wetlands. Intensification of crop production can have an impact on both aspects. It can increase GHG emissions per area because of increased fertilizer application rates. But it may also protect natural and carbon-rich areas from being converted into agricultural land because intensive crop production allows for high yields per hectare.Materials and methods – “carbon footprint” calculation based on life-cycle assessment (LCA) principlesA carbon footprint is “the total set of GHG (greenhouse gas) emissions caused directly and indirectly by an individual, organization, event or product” (Carbon Trust, 2007). This study calculates the carbon footprint per ton of winter wheat. The calculation is based on life-cycle assessment (LCA) principles. It includes all on-farm activities to produce wheat grain, theproduction and supply of seeds, pesticides, machinery, and fertilizers as well as the extraction and processing of any raw materials needed (Brentrup et al., 2004).The results presented in this paper are based on a life-cycle assessment (LCA) study (Brentrup et al., 2004) that uses data from a long-term comparison of increasing rates of ammonium nitrate (AN) application to winter wheat (“Broadbalk Experiment” in Rothamsted, UK). The grain yield increased from 2.1 t/ha at zero N application to a maximum of 9.3 t/ha at 240 kg N/ha. The economic optimum N application rate is at about 195 kg N/ha. The following analysis will focus on four production intensities, which are “without N” (0 kg N/ha, 2.07 t grain/ha), “50% of optimum N” (96 kg N/ha, 7.11 t grain/ha), “economic optimum N rate” (192 kg N/ha, 9.25 t grain/ha), and “optimum N + 50%” (288 kg N/ha, 9.11 t grain/ha). The N fertilizer used in this field trial is ammonium nitrate (33.5% N).ResultsFigure 3 shows the emissions of GHG per ha. For fertilizer production average European technology for ammonium nitrate production according to Jenssen & Kongshaug (2003) has been assumed.Figure 3:2ha (including production and transport of farming inputs) at different N fertilizing intensities The GHG emission for “optimum N + 50%”, “economic optimum N rate”, “optimum N – 50%”, and “without N” is 3588, 2516, 1569, and 295 kg CO2eq/ha, respectively. The “optimum N + 50%” treatment shall not be considered further, since any N application beyond the economic optimum increases GHG emissions without increasing grain yield.Crop production causes GHG emissions, but at the same time the crops fix about 1.6 tonnes of carbon dioxide per tonne of biomass through photosynthesis (Greef et al., 1993). At a yield of 18.5 t/ha (grain plus straw at economic optimum N rate) this amounts to 29.6 t CO2 fixation per ha, i.e. almost 12 times the CO2emissions. If this biomass is used as bio-fuel (e.g. for direct incineration) and thereby avoids the use of fossil fuels, a substantial net saving of CO2 emissionscan be achieved. However, by far most of the grain is still consumed as food or feed and in this case the CO2 fixation is only short- to medium-term and is usually not considered as a credit.In view of the current and future demand for cereals it can be assumed that any reduction in the production intensity at one place has to be compensated by additional production at another place. In many cases this results in land use changes from nature into agricultural land (IPCC, 2007 and Fig. 1). Figure 4 shows the additional CO2 emission that occur due to conversion of temperate forest into cropland and cultivation of cereals to compensate for the lower yields in the treatments “without N” and “50% of optimum”. Bellarby et al. (2008) gives data for CO2 sequestration per area for different ecosystems. For a temperate forest the value is 560 t CO2/ha, for arable land it is 300 t/ha, i.e. the conversion from temperate forest into cropland would release 260 t CO2/ha. In this study the total carbon loss was spread over a time period of 100 years, i.e. the annual CO2 loss due to land use change is 2600 kg CO2/ha.2production and transport of farming inputs, and land use change) at different N fertilizing intensitiesWithout any nitrogen input the grain yield is so low (2.07 t/ha) that the land required to compensate this yield loss would lead to CO2 emissions that are more than 4 times higher than those of the economic optimum system. Taking further into account the scarce land reserves it becomes obvious that a “zero nitrogen” system is not a viable option. But also the “optimum N minus 50%” treatment shows a higher carbon footprint if the additional land use needed to compensate lower yields is considered. It can be concluded that intensive crop production aiming at most efficient utilization of resources including agricultural land saves GHG emissions because natural land is potentially prevented from being converted into cropland.From a climate change perspective it is nevertheless important to further reduce the carbon footprint of crop production. Possibilities to reduce the GHG emissions from fertilizer use in crop production are discussed in the following section.Improving N use efficiency (NUE) to reduce the carbon footprint of crop production Increasing NUE means to increase the share of N that is taken up by the crop compared to the amount N applied to the soil. The most obvious method to reduce GHG emissions from crop production is to avoid any N application above the economic optimum N rate. Possible measures to improve NUE are for instance to adjust the N application rate to the actual crop N demand by using soil and plant analysis, and to synchronize N application with crop N uptake (e.g. through split application and “just-in-time” fertilization). Figure 5 shows the development of NUE from 1987 to 2005 for Europe based on data from FAO and EFMA statistics. NUE was defined as mineral N input / N removal by harvested crops x 100. NUE increased from 34% in 1987 to more than 60% in 2005. While the strong increase of NUE during the 1990ties was mainly due to the low N application rates in the Eastern European countries after their economic downturn, the increase of NUE during the last years can be attributed to improved N management on farms. More efficient use of organic N sources as well as a more targeted application of mineral nitrogen fertilizers is the explanation for the positive development of NUE in Europe.N use efficiency (NUE in %) = (N removal/N application) x 100 Figure 5: Development of N use efficiency in Europe from 1987 to 2005 (calculation based onFAO and IFA statistics, 2008)From 1990 to 2006, N2O emissions from agricultural soils have decreased by 67 Tg CO2eq (18%; UNFCCC, 2008; Fig. 6). Even though the development during the early 1990ties is mainly driven by decreasing N application in the Eastern European countries, the steadily decreasing N2O emissions during the last 10 years reveal a clear interdependency between improved NUE and reduced N2O emissions from soils.22006 (UNFCCC database, 2008)ConclusionsMineral N fertilizers are essential to sustain optimum yields that are required to satisfy the increasing global need for food, feed and bio-energy.The agricultural contribution to climate change is substantial, with land use change (CO2 from deforestation), cattle farming (CH4 from enteric fermentation), and crop production (N2O emissions from organic and mineral N inputs) as the major sources.Intensive crop production aiming at economic optimum N supply helps mitigating GHG emissions by preserving natural land from being converted into cropland.N use efficiency (NUE) has increased in Europe during the last 20 years. Increasing NUE contributes to decreasing GHG emissions from agriculture by reducing N2O emissions from soil. ReferencesBellarby J, B Foereid, A Hastings, P Smith, 2008: Cool Farming: Climate impacts of agriculture and mitigation potential. Greenpeace International, Amsterdam, The Netherlands.Brentrup F, J Küsters, J Lammel, P Barraclough, H Kuhlmann, 2004: Investigation of the Environmental Impact of Agricultural Crop Production using the Life Cycle Assessment (LCA) Methodology. Part II: Application of the LCA methodology to investigate the environmental impact of different N fertilizer rates in cereal production. Europ. J. Agronomy 20, 265-279.Carbon Trust, 2007: Carbon Footprinting. An Introduction for Organisations. Carbon Trust, London, UK.FAO (Food and Agriculture Organization of the United Nations), 2003: World Agriculture: towards 2015/2030. An FAO Perspective. Ed. Jelle Bruinsma, Earthscan Publications Ltd, London.FAO (Food and Agriculture Organization of the United Nations), 2006: World Agriculture: towards 2030/2050. An FAO Perspective. Interim report.FAO (Food and Agriculture Organization of the United Nations), 2008: /corp/statistics/en/Greef JM, F Hansen, G Pasda, W Diepenbrock, 1993: Die Strahlungs-, Energie- und Kohlendioxidbindung landwirtschaftlicher Kulturpflanzen – Ergebnisse und Modellrechnungen. Ber. Ldw. 71, 554-566.IFA (International Fertilizer Industry Association), 2006: IFA – Statistics - Total fertilizer consumption by region (N + P2O5 + K2O). /ifa/statistics/indicators/IPCC (Intergovernmental Panel on Climate Change), 2006: 2006 IPCC Guidelines for National Greenhouse Gas Inventories. Volume 4. Agriculture, Forestry and Other Land Use. IGES, Hayama, Japan.IPCC (Intergovernmental Panel on Climate Change), 2007: Technical Summary. In: Climate Change 2007: The Physical Science Basis. Contribution of Working Group I to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change [Solomon, S., D. Qin, M. Manning, Z. Chen, M. Marquis, K.B. Averyt, M. Tignor and H.L. Miller (eds.)].Cambridge University Press, Cambridge, United Kingdom and New York, NY, USA.Jenssen & Kongshaug, 2003: Energy consumption and greenhouse gas emissions in fertiliser production. IFS (The International Fertiliser Society) Proceedings No:509. IFS, York, UK. UNFCCC (United Nations Framework Convention on Climate Change), 2008: http://unfccc.int/ghg_data/ghg_data_unfccc/items/。

矿物质掺合料混凝土在橡胶坝工程中的应用

矿物质掺合料混凝土在橡胶坝工程中的应用

矿物质掺合料混凝土在橡胶坝工程中的应用摘要:根据滦河迁安市段生态防洪工程4号橡胶坝工程矿物质掺合料混凝土施工中的效果,结合混凝土施工中各个环节,寻求矿物质掺合料混凝土在水利工程中合理应用。

关键词:矿物质;橡胶坝;控制abstract: according to the effect of mineral admixtures concrete construction of the no.4 rubber dam project on qian’an section of luanhe river, and combining with the each link of concrete construction, in this paper, the author seeks for the proper application of mineral admixtures concrete in water conservancy engineering.keywords: minerals; rubber dam; control中图分类号:tu377文献标识码: a 文章编号:1.工程概况滦河迁安市段生态防洪工程4号橡胶坝工程,位于滦河回水窝出口下游处,河道较宽,主河槽靠近左岸,平面形态宽浅散乱,多枝杈;地质条件复杂,混凝土极易受到硫酸根离子侵蚀、氯离子侵蚀及冻融破坏等;本工程采用矿物质掺和料混凝土是防止破坏的措施之一,结合混凝土配合比、原材料、以及混凝土的拌合、运输、浇筑、养护等方面入手加强施工工艺控制,通过多种技术措施来保证橡胶坝主体混凝土的耐久性。

2.配合比控制⑴在混凝土中适量掺入优质粉煤灰等矿物质掺合料,改善混凝土的工作性和耐久性。

⑵掺入减水率高、适量引气、坍落度损失较小,能明显改善或提高混凝土耐久性的聚羧酸高性能外加剂,外加剂的用量严格按设计配合比掺加,防止使用过量对混凝土产生不利的影响。

粉煤灰混凝土的氯离子结合性能

粉煤灰混凝土的氯离子结合性能

粉煤灰混凝土的氯离子结合性能孙丛涛;宋华;牛荻涛;张鹏;侯保荣【摘要】采用干湿交替方式研究了粉煤灰混凝土的氯离子结合性能,得到了混凝土中自由氯离子含量和总氯离子含量的分布,探讨了粉煤灰对氯离子结合性能的影响,分析了氯离子结合性能随深度的变化规律.结果表明:粉煤灰的掺入提高了混凝土中的结合氯离子含量,但粉煤灰混凝土的氯离子结合率和相对氯离子结合系数均低于未掺粉煤灰混凝土,且两者均随着粉煤灰掺量的增加呈降低趋势;混凝土中结合氯离子含量随深度的增加呈先降低再升高的趋势;氯离子结合能力随深度的增加呈上升趋势并逐渐趋于平稳.【期刊名称】《建筑材料学报》【年(卷),期】2016(019)001【总页数】5页(P35-39)【关键词】氯离子结合性能;自由氯离子;总氯离子;粉煤灰混凝土;扩散深度【作者】孙丛涛;宋华;牛荻涛;张鹏;侯保荣【作者单位】中国科学院海洋研究所,山东青岛266071;青岛理工大学土木工程学院,山东青岛266033;西安建筑科技大学土木工程学院,陕西西安710055;青岛理工大学土木工程学院,山东青岛266033;中国科学院海洋研究所,山东青岛266071【正文语种】中文【中图分类】TU528.1氯离子入侵引起的钢筋锈蚀是海洋环境和除冰盐环境中混凝土结构耐久性破坏的主要原因,致使多数结构未达到设计使用年限即发生耐久性失效或者破坏,造成了巨大经济损失.环境中的氯离子会渗透到混凝土内部,一部分以自由离子的形式存在于孔溶液中,另一部分与孔壁中水泥的水化产物等发生化学结合或物理吸附[1].混凝土对氯离子的化学结合和物理吸附作用统称为混凝土的氯离子结合性能.氯离子结合性能一方面影响氯离子在混凝土中的传输,另一方面影响钢筋锈蚀的临界氯离子含量[2].因此,氯离子结合性能对混凝土结构的使用寿命预测至关重要,开展混凝土的氯离子结合性能研究对于结构耐久性寿命预测模型的建立及耐久性设计意义深远.随着粉煤灰在混凝土中的广泛应用,粉煤灰混凝土的氯离子结合性能已成为学者研究的重点.陈书苹等[3-6]采用平衡法研究了浆体的氯离子结合性能,结果表明粉煤灰的掺入可有效改善水泥基材料的氯离子结合性能.Cheewaket等[7]通过3,4,5,7a的混凝土暴露试验表明,氯离子结合能力随着粉煤灰掺量的增加而增加.Hu 等[8-10]通过实验室全浸泡或干湿循环方式研究了粉煤灰混凝土的氯离子结合性能,结果显示随着粉煤灰掺量的增加,混凝土的氯离子结合能力呈先上升后下降的变化趋势,Dhir等[11]采用平衡法也证明了这一点.然而,刘军等[12]采用内掺氯离子的方式研究表明,粉煤灰的掺入降低了氯离子结合能力,且粉煤灰掺量越大,氯离子结合能力下降越多.Nagataki等[13]的研究也表明30%粉煤灰掺量1)降低了水泥基材料的氯离子结合能力.由此可见,有关粉煤灰对氯离子结合性能影响的研究结论并不一致,因此对粉煤灰混凝土的氯离子结合性能还需进一步的研究.本文采用干湿交替方式研究了粉煤灰混凝土的氯离子结合性能,深入探讨了粉煤灰的掺入对混凝土氯离子结合性能的影响,并分析了氯离子结合性能随深度的变化规律.1.1 原材料及混凝土配合比混凝土原材料为:P·O 42.5普通硅酸盐水泥,Ⅱ级粉煤灰,细度模数为2.62的河砂,粒径为5~20mm的碎石,自来水.胶凝材料化学组成见表1,混凝土配合比见表2.1.2 试验方法试件成型24h后拆模,标准养护28d,然后在(19±3) ℃,相对湿度(75±3)%条件下自然养护至90d.取100mm×100mm×300mm的试件,只留一个长方形侧面作渗透面,其余面用石蜡密封.试件在质量分数为3.5%的NaCl溶液中浸泡7d,再在(22±6) ℃,相对湿度(78±6)%的自然条件下晾干 7d,此为1个干湿循环,每个试件共进行10个干湿循环.切取待测试件中部100mm区段并沿其渗透面逐层磨取粉样,深度不大于10mm时每1mm取一次样,深度大于10mm时每2mm取一次样,最后参照JTJ 270—1998《水运工程混凝土试验规程》中的试验方法测定粉样中的自由氯离子含量和总氯离子含量.2.1 氯离子含量随深度分布情况环境中的氯离子通过混凝土保护层到达钢筋表面,聚集到一定含量时将引起钢筋脱钝锈蚀,因此氯离子在混凝土中的含量分布是评价混凝土抗氯离子侵蚀性能的重要参考.图1,2分别为混凝土中自由氯离子含量(Cf)和总氯离子含量(Ct)随深度的分布曲线.由图1,2可见,自由氯离子含量和总氯离子含量随深度的变化趋势一致,均呈先增加后降低最后趋于平稳的变化趋势.其原因是周期性暴露于海水或者氯盐溶液的混凝土内部按氯离子迁移方式的不同可分为3个区域:(1)对流区(氯离子含量分布曲线上升段),氯离子主要以毛细吸附和水分蒸发形成的对流方式迁移;(2)扩散区(曲线下降段),氯离子主要以扩散方式向混凝土内部传输;(3)外界氯离子未渗入区(曲线近乎水平段),氯离子主要随原材料混入混凝土内部.2.2 粉煤灰对氯离子结合性能的影响目前,相关研究中表征混凝土氯离子结合性能的参数并不统一,这可能是造成粉煤灰对混凝土氯离子结合性能影响的研究结论不一致的原因所在.1)文中所涉及的掺量、含量等均为质量分数.常用的表征参数主要有单位质量混凝土或灰浆的结合氯离子含量Cb(Cb=Ct-Cf)[14]、氯离子结合率f(f=(Cb/Ct)×100%)[12]和相对氯离子结合系数S(S=Cb/Cf)[15].表3给出了各配合比混凝土在4,8mm深度处的结合氯离子含量、氯离子结合率和相对氯离子结合系数.由表3可见,在4,8mm深度处,除个别数据外,粉煤灰混凝土的结合氯离子含量均高于未掺粉煤灰混凝土,这说明粉煤灰的掺入提高了混凝土的氯离子结合性能.一方面,这是因为粉煤灰中的活性组分与水泥水化产物Ca(OH)2反应生成的C-S-H凝胶提高了混凝土对氯离子的物理吸附作用,反应生成的水化铝酸钙改善了混凝土对氯离子的化学结合作用,且粉煤灰消耗了水泥水化产物Ca(OH)2,使混凝土内部pH值降低,有利于氯离子的结合[16];同时,粉煤灰所具有的空心结构和复杂的内比表面积,有助于粉煤灰和C-S-H凝胶的物理吸附以及水化铝酸钙的化学结合作用[17].另一方面,粉煤灰的掺入降低了混凝土中各组分的含量,减少了C-S-H凝胶和水化铝酸钙的生成,从而对混凝土的氯离子结合性能产生了不利影响.排除其他因素的影响,在上述两方面因素的比较中,显然前者占据了主导地位,即粉煤灰的掺入有助于提高混凝土的氯离子结合性能.由表3还可见,粉煤灰混凝土的氯离子结合率和相对氯离子结合系数均低于未掺粉煤灰混凝土,且随着粉煤灰掺量的增加呈降低趋势.由此可以认为,粉煤灰的掺入降低了混凝土的氯离子结合性能.从上述分析可见,以氯离子结合率和相对氯离子结合系数作为氯离子结合性能衡量指标得出的结论与以结合氯离子含量为指标得出的结论截然相反.这是因为除混凝土特性外,氯离子含量也是影响其结合性能的重要因素.根据吸附的相关理论[3],吸附量与吸附质含量关系密切.吸附量随着溶液中吸附质含量的增大而增加,即混凝土孔溶液中自由氯离子含量越高,孔隙壁接触氯离子的几率就越大,氯离子的结合量就越大,而此时每个氯离子被结合的几率较低,因此结合氯离子含量与孔溶液中自由氯离子含量的比值较小.反之,混凝土孔溶液中自由氯离子含量越低,每个氯离子被结合的几率越高,此时结合氯离子含量与自由氯离子含量的比值较大.基于上述理论,粉煤灰混凝土中结合氯离子含量应高于未掺粉煤灰混凝土,且由图1,2可见,在4,8mm深度处,粉煤灰混凝土中自由氯离子含量和总氯离子含量也均高于未掺粉煤灰混凝土,宏观上即表现为粉煤灰混凝土的氯离子结合率和相对氯离子结合系数均低于未掺粉煤灰混凝土.综上所述,衡量混凝土氯离子结合性能的指标既要考虑材料的氯离子结合能力又不能忽略孔溶液中自由氯离子含量的影响,因此,由结合氯离子与自由氯离子含量的比值S(相对氯离子结合系数)来表征混凝土的氯离子结合性能更为合理(以下分析中的氯离子结合能力均指比值S).由此可以得出结论,混凝土氯离子结合能力由于粉煤灰的掺入而降低,且随粉煤灰掺量的增大而逐渐降低.2.3 氯离子结合性能随深度变化规律图3为混凝土中结合氯离子含量随深度分布曲线.由图3可见,混凝土中结合氯离子含量随深度的增加呈先降低再升高的趋势.结合图1,2可见,结合氯离子含量最低处基本对应氯离子含量分布曲线的拐点部位(即外渗氯离子所达深度处).在氯离子含量分布曲线上升段和下降段,结合氯离子源于内掺和外渗氯离子;在曲线的水平段,结合氯离子主要来自内掺氯离子.对于内掺氯离子,氯离子的结合在 28d 内基本完成[18],由此说明试件在接触外界氯离子前已基本完成对内掺氯离子的结合.Nagataki等[13]研究表明混凝土对外渗氯离子的结合能力为其对内掺氯离子的2~3倍.由图1~3可见,混凝土中结合氯离子含量随外渗氯离子含量的降低而先降低再升高,当外渗氯离子含量较高时(深度约4~10mm 处),其渗入提高了混凝土中的结合氯离子含量,而当外渗氯离子含量较低时(深度约10~14mm 处),其渗入却降低了结合氯离子含量,由此形成了结合氯离子含量的谷底.据此可以推断,当混凝土中存在内掺氯离子时或许存在一个外渗氯离子临界值,低于此临界值时,外渗氯离子会降低混凝土中结合氯离子含量,高于此临界值时,外渗氯离子会提高混凝土中结合氯离子含量,其机理有待进一步研究.图4为氯离子结合能力随深度变化曲线.由图4可见,随着深度增加,氯离子结合能力呈上升趋势并逐渐趋于平稳,这与金祖权等[19]研究结论基本一致.而吴庆令等[20]发现氯离子结合能力随深度上升并趋于平稳后,在深层又呈现再次增长趋势,其原因未作分析.然而,Hu等[8-10]和Mohammed等[21]利用自由氯离子含量与总氯离子含量之间的线性关系,认为氯离子结合能力不随深度变化而变化.本文计算分析发现,各试件中自由氯离子含量与总氯离子含量之间存在良好线性关系,即:式中:K为系数.由氯离子结合能力S的表达式和式(1)可得:通过式(2)计算可得试件FA1~FA4的氯离子结合能力分别为0.1537(相关系数R=0.9991),0.1258(R=0.9997),0.0679(R=0.9997)和0.1034(R=0.9995).将此结果与表3和图4对比可见,通过线性关系得到的氯离子结合能力可在一定程度上反映混凝土的氯离子结合性能,但所反映的性能仅限混凝土表层区域,即混凝土中氯离子含量较高区域,而对于深层区域,通过线性关系得到的结果会低估其氯离子结合能力.(1)粉煤灰的掺入提高了混凝土中的结合氯离子含量,但粉煤灰混凝土的氯离子结合率和相对氯离子结合系数均低于未掺粉煤灰混凝土,且两者均随着粉煤灰掺量的增加呈降低趋势.以结合氯离子含量与自由氯离子含量的比值来表征混凝土的氯离子结合性能更为合理.(2)混凝土中结合氯离子含量随深度增加呈先降低再升高的趋势,氯离子结合能力随深度增加呈上升趋势并逐渐趋于平稳.(3)通过混凝土中自由氯离子含量与总氯离子含量的线性关系计算得到的氯离子结合能力可在一定程度上反映混凝土的氯离子结合性能,但会低估混凝土除表层外其他深度处的氯离子结合能力.【相关文献】[1] RAMACHANDRAN V S.Possible states of chloride in the hydration of tricalcium silicate in the presence of calcium chloride[J].Matériaux et Constructions,1971,4(19):3-12. 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矿产资源的英语作文

矿产资源的英语作文

矿产资源的英语作文The Importance and Sustainable Exploitation of Mineral Resources.Mineral resources are a crucial component of our global economy, serving as the backbone of various industries such as construction, manufacturing, and energy production. These resources, including metals, fossil fuels, and non-metallic minerals, are extracted from the Earth's crust to fuel our modern way of life. However, their extraction and utilization present significant challenges, especially in terms of sustainability and environmental impact.The Economic Value of Mineral Resources.The economic value of mineral resources cannot be overstated. Metals such as iron, copper, and aluminum are essential for building infrastructure, automobiles, and machinery. Fossil fuels like coal, oil, and natural gas power our factories, heat our homes, and fuel ourtransportation systems. Without these resources, the industrialized world would grind to a halt.Moreover, the mining industry generates significant employment opportunities and revenue for governments. Mining companies employ millions of people worldwide, providing stable jobs in often remote and rural areas. Additionally, mineral exports are a major source of foreign currency for many developing countries, contributing to their economic growth and development.Environmental Challenges and Sustainability Concerns.However, the extraction of mineral resources is not without its costs. Mining operations can have devastating effects on the environment, including soil erosion, water pollution, and habitat destruction. The extraction offossil fuels contributes significantly to climate change, as the burning of these fuels releases vast amounts of greenhouse gases into the atmosphere.Sustainability is therefore a crucial consideration inthe mining industry. Many mining companies are now adopting greener practices, such as using more efficient extraction methods, recycling water and waste materials, and rehabilitating mined areas to minimize environmental damage. Additionally, there is a growing focus on developing renewable energy sources to reduce our reliance on fossil fuels.Innovations in Mineral Extraction.Innovations in technology are helping to make themining industry more sustainable. Advanced drilling and extraction techniques allow for more efficient and precise mining, reducing waste and environmental impact. Automation and robotics are being increasingly used in mines, reducing the need for human labor in hazardous environments.Moreover, new technologies are being developed toextract minerals from low-grade ores or even waste materials, increasing the overall efficiency of the mining process. This not only reduces waste but also extends the lifespan of mines, delaying the need for new ones.Conclusion.Mineral resources are essential to our modern way of life, but their extraction and utilization must be balanced with environmental sustainability. By adopting greener practices, using innovative technologies, and developing renewable energy sources, we can ensure that we continue to benefit from these resources while protecting our planetfor future generations.(Note: This article is a condensed version of the requested length. While it covers the main points, it may not meet the exact word count requirement.)。

固井低密度水泥浆用矿渣和粉煤灰反应活性对比

固井低密度水泥浆用矿渣和粉煤灰反应活性对比

固井低密度水泥浆用矿渣和粉煤灰反应活性对比肖淼 (天津中海油服化学有限公司,天津 300301)摘要:矿渣低密度水泥浆和粉煤灰低密度水泥浆在油田固井作业中应用广泛,对解决低压易漏失地层固井和提高固井作业质量及经济效益具有重要意义。

文章研究了50 ℃下矿渣和粉煤灰对低(1.50 g/cm3)密度水泥浆体早期抗压强度的影响。

水化热(ICC)测试表明,50 ℃下矿渣低密度水泥浆水化速率峰值及1 d累计放热量较粉煤灰低密度水泥浆分别增大16.7%和14.1%。

水化产物定性及定量分析观察表明,1 d龄期矿渣低密度水泥石中存在大量絮状产物C-S-H凝胶,并伴有AFt和Ca(OH)2晶体生成,且随水化反应进行AFt含量增加,养护10 d后部分AFt转化为AFm。

粉煤灰低密度水泥石中C-S-H凝胶和AFt含量从1 d至7 d逐渐增加。

随着养护龄期延长,两种低密度水泥石基体逐渐密实,水泥石抗压强度都逐渐增大,但矿渣的早期水化反应活性高于粉煤灰,使得矿渣低密度水泥石早期抗压强度高于粉煤灰低密度水泥石。

关键词:低密度水泥浆;矿渣;粉煤灰;水化活性;抗压强度中图分类号:TE25 文献标志码:A 文章编号:1008-4800(2021)15-0123-03DOI:10.19900/ki.ISSN1008-4800.2021.15.061Comparison with Hydration Activity of Slag andFly Ash Used in Low-Density Cement SlurryXIAO Miao (Tianjin CNOOC Chemical Co., Ltd., Tianjin 300301, China)Abstract: The slag low-density cement slurry and fly ash low-density cement slurry are widely used in oil well cementing, they are of great significance to solve the low pressure and easy leakage formation well cementing and improve the quality and economic benefit of well cementing. In this paper, the effects of two mineral admixtures, slag and fly ash, on the early compressive strength of 1.50 g/cm3 cement slurry at 50 ℃ were studied and characterized by hydration exothermic (ICC), hydration products and scanning electron microscopy (SEM). The ICC tests showed that the peak of hydration rate and cumulative heat release in 1 d of slag low-density cement slurry at 20 °C were 16.7% and 14.1% higher than that of fly ash low-density cement slurry, respectively. XRD and SEM tests showed that there was a large amount of flocculent product C-S-H gel in slag low-density cement stone after curing 1 d, and accompanied by the formation of AFt and Ca(OH)2 crystals. Thecontent of AFt increased with the hydration reaction, part of AFt converted to AFm after curing 10 d.The content of C-S-H gel and AFt in fly ash low-density cement stone increased from 1 d to 7 d.With the prolongation of curing age, the matrix of slag low-density cement stone and fly ash low-density cement stone gradually became compacted, and the compressive strength of cement stone gradually increased.The results showed that the hydration reaction activity of slag was higher than that of fly ash, which made the early compressive strength of the slag low-density cement stone is higher than that of the fly ash low-density cement stone.Keywords: low-density cement slurry; slag; fly ash; hydration activity; compressive strength0引言低密度水泥浆体系在低压、易漏地层的固井中已经得到广泛的应用。

高英力教授 - 长沙理工大学欢迎您!

高英力教授 - 长沙理工大学欢迎您!

高英力教授作者: 2010-04-01 15:12:48个人基本情况:姓名:高英力性别:男出生年月:1977年5月民族:汉政治面貌:党员职称职务:教授,硕士生导师,系支部书记最后学历、学位:博士研究生学历、博士、博士后工作单位:长沙理工大学交通运输工程学院办公电话:E-mail : yingligao@从事研究的学科专业领域及主要研究方向:从事研究的学科专业领域:土木工程材料主要研究方向:道路结构新材料、新型建筑材料研发、工业固体废弃物综合利用主要工作经历及业绩:1999年建筑工程专业本科毕业,获学士学位,2000年考入中南大学土木建筑学院攻读硕士学位,2002年4月获得提前攻读博士学位资格,2005年12月获道路与铁道工程专业工学博士学位,2006年1月进入武汉理工大学材料学院进行博士后研究工作,2008年3月博士后出站进入长沙理工大学交通运输工程学院。

2013.5~2014.5,作为国家公派访问学者,在加拿大Ryerson University 留学访问。

主要从事建筑材料的科研与教学工作,承担了本科生《土木工程材料》、《建筑材料》、《工程复合材料》等课程的教学任务。

在科研方面,多年来一直从事土木工程结构高性能水泥基材料、道路工程新材料方面的研究工作,包括:①道路结构新材料的研发及应用;②公路路面高性能水泥混凝土及沥青混凝土研究及应用;③工业固体废弃物综合利用;④地下工程隧道衬砌结构设计、开发、研究与应用。

⑤混凝土用高性能化学外加剂研究及应用等。

先后主持或参加了国家及省部级科研项目10余项。

发表科研学术论文70余篇,其中SCI、EI、ISTP检索达32篇次,申请国家发明专利10项,其中已授权专利8项。

作为项目负责人和主要参加人获省部级奖励7项。

目前主持的主要科研项目:①湖南省自然科学基金项目“碳化、氯盐及荷载耦合作用下钢筋轻骨料混凝土劣化过程及机理研究(编号13JJ3070)”②湖南省交通科技计划项目“湘西地区低温潮湿沥青路面防冻抗滑关键材料设计及施工技术研究”③教育部博士点基金项目“非荷载多因素作用下高强混凝土微裂缝演化机制的工业CT 研究”(编号:20104316120001)④湖南省教育厅重点项目“相变控温梯度复合水泥混凝土路面结构及性能研究” (编号:11A005)⑤中国博士后科学基金特别资助项目“梯度复合混凝土界面区微裂缝动态演化机制的工业CT研究”(编号:201003507)⑥长沙理工大学特殊环境道路工程湖南省重点实验室开放基金资助项目“高强轻骨料混凝土微裂缝动态演化机制的CT研究”(编号:kfj110407)已完成的主要科研项目:作为主持或主要完成人,完成主要科研项目及成果包括:①“水泥混凝土结构材料功能优化及其在公路工程中的应用技术研究”,通过湖南省科技厅组织的技术成果鉴定,成果整体国际先进,部分国际领先,项目主持②湖南省自然科学基金项目“功能梯度水泥基材料界面特征及体积变形机理研究(编号09JJ4023)”,项目主持③中国博士后科学基金面上项目“梯度复合混凝土界面区体积变形与整体性能劣化的相关性(编号20090450986)”,项目主持④湖南省交通厅科技项目子项“冰雪气候下桥梁的桥面抗滑技术探索研究”,项目主持⑤中国博士后科学基金面上项目“复杂环境下超细粉煤灰功能梯度混凝土体积变形及机理研究(编号20070410969)”,项目主持⑥国家973项目“高性能水泥制备和应用”子题:“化学外加剂对高性能水泥水化及结构的作用机理”(编号:2001CB610704),技术负责⑦国家863计划:“高抗渗长寿命大管径隧道管片材料结构设计与工程应用”(编号:2005AA332010),技术负责⑧国家十五科技攻关项目:“新型高性能混凝土及其耐久性的研究”课题“不同强度等级水泥配制高性能混凝土的研究(编号:2001BA307B0302-03)”,技术负责⑨重庆交通大学(桥梁)结构工程重点实验室开放基金项目“盾构隧道衬砌管片功能梯度设计及性能优化研究”(编号CQSLBF-Y07-1),项目主持⑩湖北省博士后科研活动专项资助计划项目“隧道管片功能梯度设计方法与优化技术”(编号:408-32305),项目主持11长沙理工大学博士科研启动基金项目“梯度复合混凝土收缩变形及抗裂性研究”(编号1004212),项目主持12武汉理工大学科学研究基金自由探索类项目: “功能梯度水泥基材料界面特征及体积变形研究”(编号:xjj2007033),项目主持13长沙理工大学道路结构与材料交通行业重点实验室开放基金资助项目“功能梯度混凝土的界面特征与变形机理”(编号:kfj080208),项目主持完成的主要论文:1. Gao Ying-li, MA Baoguo, ZHOU Shiqiong. Production and Engineering Application of C60 High-Performance Pump Pebble Concrete Containing Ultra-Fine Fly Ash [J]. Canadian Journal of Civil Engineering, 2008, 35(8): 757-763. (SCI, EI收录)2 Gao Ying-li, Cheng Ling. Effects of different mineral admixtures on carbonation resistance of lightweight aggregate concrete, Construction and Building Materials, 2013, 43: 506-510. (SCI,EI收录)3 Gao Ying-li, Zhang Hai-lun. Study on early autogenous shrinkage and crack resistance of fly ash high-strength lightweight aggregate concrete. Magazine of Concrete Research, 2013, 65(15): 906-913. (SCI, EI收录) 4. Gao Ying-li, Zhou Shi-qiong. Influence of Ultra-Fine Fly Ash on Hydration Shrinkage of Cement Paste. Journal of Central South University of Technology (English edition), 2005, 12(5): 596-600. (SCI,EI收录) 5. Gao Ying-li, Zhou Shi-qiong, Yin Jian. Integrated utilization of ultra-fine fly ash - Fluoro gypsum for highway repair. Key Engineering Materials, 2006, v302-303: 255-262. (SCI,EI收录)6. Gao Ying-li, Ma Bao-guo, Cai Mao-tao. Finite Element Analysis of shrinkage in the Interface of Functionally Graded Concrete Segment Used in Shield Tunneling. Journal of Wuhan University of Technology-Materials Science, 2006, 21(Suppl.): 94-98. (SCI、EI收录)7. Gao Ying-li, Ma Bao-guo. Production of high-performance composite concrete segment and experimental investigation of materials. Advanced Materials Research, 2011, (168-170): 1042-1045. (EI收录)sequestration property of cement 8. Gao Ying-li, Chen Ling. Study on CO2based composite cementitious materials containing steel slag used in road. Advanced Materials Research, 2011, 311-313(8): 1949-1952. (EI收录)9. 高英力, 胡柏学, 贺敬, 杨文剑. 相变控温水泥混凝土路面板设计及模型试验. 中国公路学报, 2011, 24(2): 13-16. (EI收录)10. 高英力, 马保国, 王信刚, 等. 盾构隧道功能梯度混凝土管片的研发及性能研究. 岩石力学与工程学报, 2007, 26(11): 2341-2347. (EI收录)11. 高英力, 周士琼, 马保国. 铁路桥梁用超细粉煤灰高性能混凝土的试验研究. 铁道学报, 2006, 28(3):121-127. (EI收录)12. 高英力, 马保国, 王信刚. 钢筋保护层混凝土细观界面过渡区优化及耐久性. 土木建筑与环境工程, 2009, 31(4): 19-24. (EI收录)13. 高英力, 陈瑜. 粉煤灰-脱硫石膏水泥基材料水化活性及微结构. 土木建筑与环境工程, 2011, 33(5): 137-142. (EI收录)14. 高英力, 马保国, 周士琼. UFA道路混凝土早期自收缩及开裂敏感性研究. 沈阳建筑大学学报, 2007, 23(2): 271-275. (EI收录)15. 高英力, 马保国, 周士琼. UFA水泥基材料早期自干燥及自收缩研究. 武汉理工大学学报, 2007, 29(3): 45-49. (EI收录)16. 高英力, 周士琼, 马保国. UFA水泥基材料早期自收缩与干燥收缩研究. 深圳大学学报(理工版), 2008, 25(1): 97-102. (EI收录)17. 高英力, 陈瑜, 马保国, 等. 脱硫石膏-粉煤灰活性掺合料设计及水化特性. 四川大学学报(工程科学版), 2010, 42(2):225-231. (EI收录)18. 马保国, 高英力, 王信刚, 等. 无细观界面过渡区水泥基材料的设计及性能. 硅酸盐学报, 2007, 35(7): 886-892. (EI收录)19. 周士琼, 高英力, 尹健. 道路用复合超细粉煤灰的应用研究. 建筑材料学报, 2004, (7):311-316.(EI收录)已授权主要专利:1. 高英力. 一种含相变储能材料的防冻抗滑混凝土路面板, 专利号: ZL 2010 2 0142424.9.2. 高英力, 贺敬, 杨文剑, 杜月凡, 汪文渊. 一种具有梯度功能的高耐久混凝土路面板. 专利号: ZL 2010 2 0142449.9.功能的混凝土路面材料、路面3. 高英力, 程领. 具有吸附固化汽车尾气中CO2及其制备和应用方法. 专利号: ZL 2011 1 0029970.0.4. 高英力等. 水泥基复合材料硬化后体积变形实时测试装置及方法. 专利号: ZL 2013 2 0063365.X.5. 马保国, 高英力, 王信刚, 王凯, 金宇, 罗忠涛. 盾构隧道混凝土管片的功能梯度材料界面强化工艺. 专利号: ZL 2006 1 0019657.8.6. 马保国, 高英力, 王信刚, 王凯, 金宇, 罗忠涛. 一种利用FRP筋强化盾构管片的功能梯度材料界面的工艺. 专利号: ZL 2006 1 0124482.7.7. 马保国, 高英力, 王信刚, 王凯, 金宇, 罗忠涛. 盾构隧道管片的保护材料及其制备方法. 专利号: ZL 2006 1 0124481.2.8. 高英力, 陈瑜. 一种粉煤灰-脱硫石膏-水泥自膨胀抗裂型干粉砂浆及其制备方法. 专利号: ZL 2009 1 0042971.1.科研获奖:中国公路学会科技进步二等奖, “水泥混凝土结构材料功能优化及其在公路工程中的应用技术研究”,2014年,排名1;中国公路学会科技进步二等奖, “水泥基复合材料多尺度理论及应用技术”,2011 年,排名2;湖南省科学技术进步三等奖, "土木工程结构材料多尺度理论、耐久性优化及核心应用技术",2013年,排名2;教育部高等学校科学研究优秀成果科学技术进步二等奖, “高抗渗长寿命大管径隧道管片材料关键制备技术与应用”;2010年,排名6;教育部高等学校科学研究优秀成科学技术进步奖二等奖, “高掺量硅铝质固体废弃物制备承重墙体材料的关键技术与成套装备”;2007年,排名9;中国公路学会科技进步三等奖, “燃煤电厂工业固体废料脱硫石膏-粉煤灰综合开发及利用”,2010 年,排名2;中国公路学会科技进步二等奖, “高速公路隧道路面结构与材料应用技术研究”,2010 年,排名9 。

替代能源的影响英语作文

替代能源的影响英语作文

替代能源的影响英语作文1. The impact of alternative energy sources on the environment is undeniable. Renewable energy such as solar and wind power can help reduce greenhouse gas emissions and combat climate change.2. In addition to environmental benefits, alternative energy sources can also create new job opportunities and stimulate economic growth. The renewable energy sector is rapidly expanding, providing employment for many people around the world.3. The use of alternative energy sources can reduce our dependence on fossil fuels, which are finite resources that contribute to air and water pollution. By transitioning to cleaner energy sources, we can improve public health and quality of life.4. One of the challenges of alternative energy sources is their intermittent nature. Solar and wind powergeneration can be affected by weather conditions, leading to fluctuations in energy supply. This highlights the need for energy storage solutions to ensure a reliable and stable power supply.5. Governments and businesses are increasinglyinvesting in research and development of alternative energy technologies to address these challenges. Innovation in the renewable energy sector is crucial for achieving a sustainable energy future.6. The transition to alternative energy sources requires a shift in mindset and behavior. Individuals can contribute to the adoption of clean energy by reducing energy consumption, supporting renewable energy policies, and advocating for sustainable practices in their communities.7. Overall, the widespread adoption of alternative energy sources has the potential to transform our energy systems and create a more sustainable future for generations to come. By embracing clean energy solutions,we can protect the environment, promote economic growth, and improve the well-being of society as a whole.。

不同矿物掺合料对改性硫氧镁水泥性能影响的研究

不同矿物掺合料对改性硫氧镁水泥性能影响的研究

第41卷第1期2022年1月硅㊀酸㊀盐㊀通㊀报BULLETIN OF THE CHINESE CERAMIC SOCIETY Vol.41㊀No.1January,2022不同矿物掺合料对改性硫氧镁水泥性能影响的研究闫浩康,王㊀硕,时绪智,袁兴栋,隋玉武,岳雪涛(山东建筑大学材料科学与工程学院,济南㊀250101)摘要:为探究矿物掺合料对改性硫氧镁水泥的影响及作用机理,分别将不同掺量的粉煤灰㊁矿粉掺入改性硫氧镁水泥中,对其力学性能㊁耐水性和耐酸性进行测试,并结合X 射线衍射和扫描电镜对其物相组成及微观形貌进行表征和分析㊂研究结果表明:粉煤灰的掺入会提高改性硫氧镁水泥的3d 强度,但后期强度有所下降,当粉煤灰掺量大于20%(质量分数)时,其28d 抗压强度相较于基准组损失了14.7%;掺入矿粉对改性硫氧镁水泥的前期强度影响较小,并导致后期强度下降,当矿粉掺量为30%~40%(质量分数)时,水泥的28d 强度损失率高达17.3%㊂适量的粉煤灰与矿粉均能够提升改性硫氧镁水泥的耐水性和耐硫酸腐蚀性,其中水泥的耐硫酸腐蚀性随着粉煤灰掺量的增加而增强,耐硫酸腐蚀效果最好时矿粉掺量为20%㊂关键词:镁质胶凝材料;改性硫氧镁水泥;矿物掺合料;粉煤灰;矿粉;耐水性能;耐酸性能;力学性能中图分类号:TU526;TQ177.5㊀㊀文献标志码:A ㊀㊀文章编号:1001-1625(2022)01-0027-06Effects of Different Mineral Admixtures on Properties of Modified Magnesium Oxysulfate CementYAN Haokang ,WANG Shuo ,SHI Xuzhi ,YUAN Xingdong ,SUI Yuwu ,YUE Xuetao (School of Materials Science and Engineering,Shandong Jianzhu University,Jinan 250101,China)Abstract :In order to investigate the effect of mineral admixtures on modified magnesium oxysulfate cement and its mechanism,different amounts of fly ash and mineral powder were blended into the modified magnesium oxysulfate cement,and the mechanical properties,water resistance and acid resistance were studied.The composition and microstructure of the material phase were characterized and analyzed by X-ray diffraction and scanning electron microscopy,respectively.The results show that the incorporation of fly ash will increase the 3d strength of modified magnesium oxysulfate cement,and the later strength decreases,its 28d compressive strength loses 14.7%compared with the reference group when the fly ash dosage is more than 20%(mass fraction).The incorporation of mineral powder has little effect on the preliminary strength of modified magnesium oxysulfate cement,and makes the later strength decrease,and the 28d strength loss rate of the cement is as high as 17.3%when the mineral powder dosage is 30%to 40%(mass fraction).Both fly ash and mineral powder are able to enhance the water resistance and sulfuric acid corrosion resistance of modified magnesium oxysulfate cement,where the corrosion resistance of cement is enhanced with the increase of fly ash admixture,and the best dosage of mineral powder with the best sulfuric acid corrosion resistance is 20%.Key words :magnesia cementitious material;modified magnesium oxysulfate cement;mineral admixture;fly ash;slag;water resistance;acid resistance;mechanical property 收稿日期:2021-08-16;修订日期:2021-10-25基金项目:山东省重点研发计划(公益性科技攻关类)(2019GSF109108)作者简介:闫浩康(1997 ),男,硕士研究生㊂主要从事绿色建材等方面的研究㊂E-mail:131****5166@通信作者:岳雪涛,博士,副教授㊂E-mail:yuexuetao@0㊀引㊀言改性硫氧镁水泥(modified magnesium oxysulfate cement)是由轻烧氧化镁㊁七水硫酸镁㊁水以及外加剂制28㊀水泥混凝土硅酸盐通报㊀㊀㊀㊀㊀㊀第41卷备的一种新型气硬性镁质胶凝材料,具有轻质高强㊁耐高温等性能[1]㊂我国目前建材行业正处在飞速发展阶段,但在生产过程中一直存在效率低㊁污染严重㊁能源消耗大等问题[2],对自然环境造成了巨大的损害㊂改性硫氧镁水泥在经过热分解后可以变为原料并得以循环利用[3],这不仅能使资源得到充分利用,也有利于国民经济发展[4],是能够满足目前水泥基材料工业节能减排㊁绿色低碳㊁转型升级等需求的一种新型镁质胶凝材料㊂对于矿物掺合料在镁水泥中的应用,国内外学者展开了广泛研究㊂吴成友[5]研究了粉煤灰对硫氧镁水泥的影响,发现粉煤灰中的SiO2能够和水泥中的Mg(OH)2反应,生成一种硅酸镁水合物凝胶,使基体更加密实㊂陈从兴等[6]研究了粉煤灰和硅灰对白云石基碱式硫酸镁水泥的影响,结果表明,粉煤灰可以改善胶砂流动性,硅灰有助于提高水泥浆体早期强度㊂李利军等[7]研究了重钙粉㊁滑石粉对碱式硫酸镁水泥的强度的影响,结果表明,重钙粉有助于水泥后期抗压强度的提升,滑石粉能够大幅度提升水泥的抗折强度㊂李文超等[8]和许园园等[9]发现固硫灰可提高改性硫氧镁水泥的抗压强度,掺入不高于10%(质量分数)的固硫灰时,水泥试件的耐水性和体积稳定性得到显著改善㊂Xu等[10]指出固硫灰中含有活性SiO2,其会与MgO 反应生成M-S-H凝胶,从而提高碱式硫酸镁水泥的抗压强度和耐水性㊂本文以改性硫氧镁水泥为基本研究对象,通过加入粉煤灰㊁矿粉等矿物掺合料,来探究工业固体废弃物在新型镁质胶凝材料中的实际应用能力,研究粉煤灰㊁矿粉对改性硫氧镁水泥力学性能㊁耐水性以及耐硫酸侵蚀性能的影响,并结合X射线衍射和扫描电镜对水泥的物相组成和微观形貌进行分析㊂1㊀实㊀验1.1㊀原材料七水硫酸镁:采用山西省南风集团生产的质量分数为99.0%的七水硫酸镁(MgSO4㊃7H2O),其分子量为246.47,为白色或无色透明的针状或斜柱状结晶体,易溶于水㊂轻烧氧化镁:采用辽宁省海城市生产的85型轻烧氧化镁,利用水合法[11]测定原料中所含活性氧化镁(α-MgO)质量分数为47%,为淡黄色或白色粉末㊂柠檬酸:采用由国药集团化学试剂有限公司生产的分析纯一水合柠檬酸(C6H8O7㊃H2O),其分子量210.14,为无色结晶或白色颗粒㊂粉煤灰(fly ash,FA):采用河北省灵寿县鼎旺矿产品加工厂生产的Ⅱ级粉煤灰,其主要成分为石英㊁氧化铝等,以球形微珠形态存在,具体化学组成和微观形貌见表1和图1(a)㊂矿粉(slag,SL):采用由灵寿县弘盛矿产品加工厂生产的S95级矿渣,其主要成分为氧化钙㊁石英等,主要形态为形状不规则的块状微粒,具体化学组成和微观形貌见表2和图1(b)㊂水:采用生活用水㊂表1㊀粉煤灰的主要化学成分Table1㊀Main chemical content of fly ashComposition CaO SiO2Al2O3MgO Fe2O3TiO2K2O Na2O Mass fraction/% 6.6847.3331.260.877.19 1.28 1.530.46表2㊀矿渣化学成分Table2㊀Main chemical content of slagComposition CaO SiO2Al2O3MgO Fe2O3TiO2K2O Na2O Mass fraction/%40.2427.1114.317.300.45 1.450.460.601.2㊀试件制备本试验中FA和SL掺量分别为轻烧氧化镁质量的0%㊁10%㊁20%㊁30%㊁40%;柠檬酸掺量为α-MgO质量的1%㊂按设计的配合比称取七水硫酸镁溶于水,得到质量分数为37%的硫酸镁溶液,即H2O和MgSO4的摩尔比为18;然后将称量好的柠檬酸加入硫酸镁溶液中,充分搅拌后,得到的均一的液体倒入水泥砂浆搅㊀第1期闫浩康等:不同矿物掺合料对改性硫氧镁水泥性能影响的研究29拌锅中,再将按摩尔比(n(α-MgO)ʒn(MgSO4)为8)称量好的轻烧氧化镁粉倒入锅中,慢搅1min,快搅2min,随后把浆体注入40mmˑ40mmˑ160mm的三联水泥胶砂试模中,在(20ʃ3)ħ㊁相对湿度为(60ʃ10)%的条件下养护,1d后脱模,然后继续在该条件下养护至规定龄期㊂图1㊀粉煤灰和矿粉的SEM照片Fig.1㊀SEM images of fly ash and mineral powder1.3㊀表征与测试试件抗压强度根据GB/T17671 1999‘水泥胶砂强度检验方法(ISO法)“进行测试㊂利用德国Bruker 生产的X射线衍射仪(D8ADVANCE)对样品进行物相分析,其中加速电压为40kV,步长0.02ʎ,扫描范围为5ʎ~80ʎ㊂本试验采用德国蔡司公司生产的SUPRA55型号热场发射扫描电子显微镜对实验样品进行断口的形貌测试㊂2㊀结果与讨论2.1㊀粉煤灰和矿粉对改性硫氧镁水泥力学性能的影响图2为分别掺入两种不同掺量的矿物掺合料制作而成的改性硫氧镁水泥在3d㊁7d和28d的抗压强度,由图可知,改性硫氧镁水泥的28d强度均会随着两种矿物掺合料的掺入而降低,并且掺合料掺量越高时,对水泥的抗压强度的影响越明显,而水泥的早期强度受矿物掺合料种类影响而有所不同㊂图2(a)可以看出掺入粉煤灰后改性硫氧镁水泥的早期3d抗压强度均有所提升,掺量为20%时强度为55.40MPa,较基准组52.2MPa提升了6.1%;图2(b)显示矿粉的掺入对改性硫氧镁水泥3d抗压强度影响不大,各掺量试件强度与基准组相差基本不超过1MPa㊂由图2还可以看出,当矿物掺合料掺量为轻烧氧化镁质量的10%和20%时,其前期强度与基准组水泥抗压强度相近,并且掺入20%粉煤灰和矿粉在养护时间到28d时强度损失量仅为1.8%和6.7%,然而当矿物掺合料掺量达到40%时,养护时间28d时两者的强度损失量分别为14.7%和17.3%㊂图2㊀各配比改性硫氧镁水泥不同龄期抗压强度Fig.2㊀Compressive strength of modified magnesium oxysulfate cement at different ages30㊀水泥混凝土硅酸盐通报㊀㊀㊀㊀㊀㊀第41卷王爱国等[12]和吴成友等[13]总结了柠檬酸改性硫氧镁水泥的水化过程,水分子在MgO颗粒表面反应形成[Mg(H2O)x(OH)]+水化膜,释放OH-(见式(1));柠檬酸与水化膜反应形成络合物,从而阻碍Mg(OH)2生成(见式(2));随后络合物与溶液中的Mg2+㊁SO42-以及OH-反应生成5Mg(OH)2㊃MgSO4㊃7H2O(5㊃1㊃7相)晶核(见式(3));晶核不断生长以及MgO漏出新的表面,促进水化反应进行(见式(4))㊂MgO(s)+(x+1)H2Oң[Mg(H2O)x OH]+(surface)+OH-(aq)(1) CA n-+[Mg(OH)(H2O)x]+(surface)ң[CA n-ңMg(OH)(H2O)x-1](surface)+H2O(2) {SO2-4ң[CA n-ңMg(OH)(H2O)x-1]4ңMg2+}(surface)+6OH-ң5Mg(OH)2㊃MgSO4㊃7H2O(nucles)+(4x-13)H2O+CA n-(3)5Mg(OH)2㊃MgSO4㊃7H2O(nucles)ң5Mg(OH)2㊃MgSO4㊃7H2O(s)(4)适量的矿物掺合料可以降低水泥水化热[14],使因放热产生的细微裂纹的数量减少,从而提高试件强度;过量的掺合料则会使水泥浆体稠度增大,导致浆体搅拌不均且不易振实,并且掺合料过量会导致单位质量中活性氧化镁含量大幅降低,水化反应中MgO与水的反应速率降低,外加剂络合层与溶液中的Mg2+㊁SO2-4接触变少,单位质量中水泥的主要水化产物5㊃1㊃7相的生成量变小,从而使强度降低㊂此外,矿物掺合料在水泥体系中的前后作用较为矛盾,在早期水泥水化程度较小,适量的矿物掺合料使得基体更加密实,试件强度略有提升,到了后期MgO水化较完全,5㊃1㊃7相成为基体强度主要因素,相同掺量的矿物掺合料对MgO 的稀释作用导致水化产物减少,填充效应的影响效果大大降低,从而使得试件后期强度比基准组试件低㊂图3为掺入矿物掺合料改性硫氧镁水泥在不同养护条件下水化的XRD谱,由图3(a)可以看出,掺入粉煤灰后对改性硫氧镁水泥的水化产物影响不大,并未有新相生成,5㊃1㊃7相的衍射峰强度低于基准组,这里可以说明掺入过多粉煤灰使得单位质量中5㊃1㊃7相的生成量变小,从而使强度降低㊂从图3(b)可以看出,掺入矿粉后水泥的Mg(OH)2晶体衍射峰明显增强,MgSO4晶体的衍射峰也略有增强,而主要强度相5㊃1㊃7相的衍射峰减弱,说明矿粉会阻碍外加剂离子与[Mg(OH)(H2O)x]+的结合,从而使得MgO大量生成Mg(OH)2,原料中MgSO4反应不完全重新凝结成为晶体而成为水泥基体的薄弱部分,并减少了5㊃1㊃7相生成,而且过量的矿粉会降低水灰比,导致水泥浆体水化不完全最终使得水泥强度大幅下降㊂图3㊀各配比改性硫氧镁水泥不同养护条件的XRD谱Fig.3㊀XRD patterns of modified magnesium oxysulfate cement with different curing conditions2.2㊀粉煤灰和矿粉对改性硫氧镁水泥耐水耐酸性能的影响将正常养护28d的试块分别置于清水和5%硫酸溶液中,浸泡7d后晾干进行强度测试,测试结果如图4所示,并根据所测强度计算试件的软化系数K,如式(5)所示㊂从图中可以看出,未掺矿物掺合料的试件在经过浸水和浸酸后抗压强度出现了大幅度倒缩,软化系数为0.80,强度仅为正常养护下28d强度的79.6%和83.2%;而掺入粉煤灰后试件的耐水性与耐酸性都有所提升,其中40%掺量的试块软化系数达到了1.01,在浸水㊁浸酸处理后强度不降反升,强度分别为正常养护28d强度的101%和108%;掺入矿粉的试件在掺量为20%时耐水效果最好,软化系数为0.90,并且耐硫酸侵蚀效果最好的掺量为10%,此时抗压强度可达正常养护28d强度的97.1%㊂㊀第1期闫浩康等:不同矿物掺合料对改性硫氧镁水泥性能影响的研究31K=f F(5)式中:K为软化系数;f为浸水后试件强度;F为养护28d试件强度㊂图4㊀各配比改性硫氧镁水泥不同养护条件的抗压强度Fig.4㊀Compressive strength of modified magnesium oxysulfate cement under different curing conditions 通过图3(a)可以看出,在经过浸水和浸酸后,基准组和掺入40%粉煤灰试件的XRD谱中并未有新相生成,5㊃1㊃7相强度也几乎没有变化,而基准组试件在经过硫酸浸泡后其Mg(OH)2衍射峰略有增强,并且MgO衍射峰强度略有减小,这是因为MgO溶解并与酸产生反应而导致水泥基体疏松,从而影响强度;图5为各配比改性硫氧镁水泥的SEM照片,结合图5(b)可以看出,掺入粉煤灰后,其火山灰效应使粉煤灰表层与改性硫氧镁水泥的5㊃1㊃7相进行搭接[14],填充毛细孔道使得基体更加密实,从而提升了耐水耐酸性能㊂图5㊀各配比改性硫氧镁水泥的SEM照片Fig.5㊀SEM images of modified magnesium oxysulfate cement with different proportions 比较掺入粉煤灰和矿粉的试件在浸泡水和稀硫酸后的XRD谱,可以看出,两者皆没有生成新的水化产物㊂由图3(b)和图5(c)可以看出,掺入40%矿粉后的试件在进行耐水测试后5㊃1㊃7相衍射峰强度大幅度降低,尤其是37.35ʎ处峰值几乎为零,而Mg(OH)2衍射峰强度大大增强,使得基体中5㊃1㊃7相晶体生长长度较短且与六方片状Mg(OH)2混杂在一起,使得基体较为疏松㊂这可能是因为矿粉中含量较多的氧化钙溶于水,使得基体致密性降低,从而使5㊃1㊃7相溶解程度较大,而粉煤灰中的氧化硅㊁氧化铝等不易溶解,保证了基体的密实程度,使其强度更高㊂3㊀结㊀论(1)掺入粉煤灰和矿粉对改性硫氧镁水泥的早期强度影响不大,但会降低水泥的28d强度㊂(2)粉煤灰和矿粉对提高改性硫氧镁水泥的耐水性和耐硫酸侵蚀有积极作用,强度损失量均小于基准组试件㊂当粉煤灰掺量为40%时,经过浸水和浸酸处理的试件强度不降反升,软化系数和耐硫酸侵蚀效果最佳;当矿粉掺量为20%时软化系数最高为0.90,对试件耐水性能提升较高,掺量为10%时,耐硫酸侵蚀效32㊀水泥混凝土硅酸盐通报㊀㊀㊀㊀㊀㊀第41卷果最佳㊂(3)粉煤灰和矿粉掺入水泥中后并没有新水化产物生成,粉煤灰仅对水泥原料起稀释作用;矿粉会阻碍水泥中强度相5㊃1㊃7相的生成,使得5㊃1㊃7相晶体长度变短,并且会促进MgO生成Mg(OH)2㊂参考文献[1]㊀WU C Y,CHEN W H,ZHANG H F,et al.The hydration mechanism and performance of modified magnesium oxysulfate cement by tartaric acid[J].Construction and Building Materials,2017,144:516-524.[2]㊀吴中伟,陶有生.中国水泥与混凝土工业的现状与问题[J].硅酸盐学报,1999,27(6):734-738.WU Z W,TAO Y S.Cement and concrete industries in China:present state and problems[J].Journal of the Chinese Ceramic Society,1999, 27(6):734-738(in 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of hydration methods of determining active magnesium oxide content[J].Journal of Salt Lake Research,2010,18(1):38-41(in Chinese).[12]㊀王爱国,楚英杰,徐海燕,等.碱式硫酸镁水泥的研究进展及性能提升技术[J].材料导报,2020,34(13):13091-13099.WANG A G,CHU Y J,XU H Y,et al.Research progress and performance improvement technology of basic magnesium sulfate cement[J].Materials Reports,2020,34(13):13091-13099(in Chinese).[13]㊀吴成友,邢赛南,张吾渝,等.碱式硫酸镁水泥水化规律研究[J].功能材料,2016,47(11):11120-11124+11130.WU C Y,XING S N,ZHANG W Y,et al.Study on hydration mechanism of basic magnesium sulfate cement[J].Journal of Functional Materials,2016,47(11):11120-11124+11130(in Chinese).[14]㊀罗轲嘉,庞瑞阳,刘潘潘.粉煤灰对碱式硫酸镁水泥性能的影响[J].青海交通科技,2019(5):115-119.LUO K J,PANG R Y,LIU P P.Effect of fly ash on properties of basic magnesium sulfate cement[J].Qinghai Jiaotong Keji,2019(5):115-119(in Chinese).。

煤矿对家乡的影响英语作文

煤矿对家乡的影响英语作文

煤矿对家乡的影响英语作文Growing up in a mining town, the impact of the coal mine on my hometown is undeniable. The constant noise of machinery and the smell of sulfur in the air have become a part of everyday life for us.The economic prosperity brought by the coal mine has been a double-edged sword. While it has provided jobs for many in the community, it has also led to environmental degradation and health issues. The once pristine landscape is now scarred by mining operations, and respiratory problems are common among residents.The influx of workers from other regions has brought diversity to our town, but it has also strained our resources and infrastructure. Housing prices have skyrocketed, and traffic congestion has become a daily frustration for locals.Despite the challenges, the coal mine has shaped theidentity of our town. It has brought us together as a community, as we work to overcome the obstacles that come with living in a mining town. The resilience and solidarity of the people here are truly inspiring.As the coal mine continues to operate, we must find a balance between economic development and environmental sustainability. It is up to us to ensure that future generations can enjoy the beauty of our hometown, while also benefiting from the opportunities that the coal mine provides.。

过度开采矿资源的英语作文

过度开采矿资源的英语作文

过度开采矿资源的英语作文English: Overexploitation of mineral resources is a pressing issue that needs to be addressed urgently. The relentless demand for metals and minerals, fueled by industrialization and economic development, has led to the unsustainable extraction of natural resources. This has resulted in serious environmental degradation, including deforestation, soil erosion, and water pollution. Not only does overexploitation harm the delicate balance of ecosystems, but it also threatens the livelihoods of local communities dependent on these resources. Additionally, the depletion of mineral resources poses a significant risk to future generations, who may not have access to essential raw materials for technological advancements and economic growth. It is imperative that we adopt sustainable mining practices, such as reducing waste generation, implementing reclamation plans, and promoting responsible consumption and production patterns, to ensure the long-term viability of our planet's mineral resources.Translated content: 矿产资源的过度开采是一个迫切需要立即解决的问题。

210998427_珍珠岩对多孔吸声材料性能的影响

210998427_珍珠岩对多孔吸声材料性能的影响

【试验研究】珍珠岩对多孔吸声材料性能的影响徐传友,王海娟,赵学超,杜 鑫(河南理工大学,河南 焦作 454003)摘要:本文通过材料复合的方法选择珍珠岩等制备多孔吸声材料。

研究了珍珠岩不同粒径、掺量对制品的力学性能、吸声性能的影响。

结果表明粒径在1.18~2.36mm,掺量在25%时制得的多孔吸声材料具有较好的综合性能。

以“惠更斯原理”和“共振吸声原理”为基础,分析了珍珠岩吸声的作用机理。

关键词:珍珠岩;吸声;粒径;掺量中图分类号:P619.279;TB39 文献标识码:A 文章编号:1007-9386(2008)05-0027-03The Effect of Pearlite on Porous Sound Absorption MaterialXu Chuanyou, Wang Haijuan, Zhao Xuechao, Du Xin(Henan Polytechnic University, Jiaozuo 454003, China)Abstract: This article through material compound method choices perlite to preparation porous sound absorption material. This study is dealt with the influence of different particle size and the quantity of perlite on the performance of mechanical capability, the sound absorption influence. The result indicates the particle size at 1.18~2.36mm mix the quantity at 25%, the porous sound absorption material has the good overall performance. Based on “the huygens' principle” and “the resonating sound absorption principle”, has analyzed the perlite sound absorption action mechanism.Key words: perlite; sound absorption; particle size; quantity1 引言环境问题是当代人类普遍关注的全球性问题。

复合矿物掺合料在混凝土中应用技术规程征求意见

复合矿物掺合料在混凝土中应用技术规程征求意见

复合矿物掺合料在混凝土中应用技术规程征求意见I believe that the application of composite mineral admixtures in concrete is a great technology advancement that can significantly improve the performance and durability of concrete structures. 复合矿物掺合料在混凝土中的应用是一项技术进步,可以显著提高混凝土结构的性能和耐久性。

One of the key benefits of using composite mineral admixtures in concrete is the ability to enhance the strength and durability of the concrete. 通过使用复合矿物掺合料,可以增强混凝土的强度和耐久性。

Additionally, the use of composite mineral admixtures can also help reduce the amount of cement needed in concrete mixtures, which can lead to cost savings and a more environmentally friendly construction process. 此外,使用复合矿物掺合料还可以减少混凝土配合中所需的水泥量,从而节省成本,使建筑过程更加环保。

Furthermore, the incorporation of composite mineral admixtures can improve the workability and cohesiveness of concrete mixtures,making them easier to place and finish. 此外,混合复合矿物掺合料可以提高混凝土配合料的可塑性和粘聚性,使其更容易施工和整理。

予吾长袖,我必善舞!

予吾长袖,我必善舞!
男 江西吉安
汉 1978.9 中共党员 未婚 CET-6 文学 编辑
全国计算机等级考试 FORTRAN 二级 足球……清华大学博士后足球队主力左后卫
高性能水泥基材料研究 清华大学土木工程系建筑材料研究所博士后、助理研究员
学 1994 年 09 月~1997 年 07 月,江西省吉安县值夏中学高中部 习 1997 年 09 月~2001 年 06 月,武汉大学本科,取得工学学士学位 经 2001 年 09 月~2003 年 06 月,武汉大学硕士研究生,取得工学硕士学位 历 2003 年 09 月~2005 年 12 月,武汉大学博士研究生,取得工学博士学位
武汉大学首届研究生十大学术之星 武汉大学优秀毕业研究生(博士)

武汉大学陶然文学社社长、《息壤》主编兼文学版编辑,在《海燕》等校内
本科

外刊物中发表数篇散文、诗歌。

《武汉大学研究生学报(自然科学与工学版)》编辑,水利水电学院研究生
研究生

学生会实践部长。
科研情况
第一部分……博士后期间主持和参与的项目
第二部分……本科、研究生期间参与的项目
[1] 横向项目:昆明市掌鸠河引水供水工程水源工程(云龙水库)遂洞、溢洪道出口消 能研究,本科期间完成,2001(该研究项目获湖北省大学生优秀科研成果奖三等奖); [2] 95 国家重点科技攻关项目(No.952200201006):提高碾压混凝土抗裂能力的研究, 2001-2003; [3] 湖北省自然科学基金:混凝土界面无机粘结胶的研究与实现,2002; [4] 湖北省自然科学基金:高效无机钢筋锚固胶的研究与实现,2004; [5] 横向项目:安徽省铜陵市牯牛背水库工程结构检测与安全评价,2003; [6] 横向项目:安徽省潜阳市红旗水库工程结构检测与安全评价,2003; [7] 横向项目:安徽省宿松市钓鱼台水库工程结构检测与安全评价,2003; [8] 横向项目:新滩口排水闸加固工程塑性混凝土研究,2003; [9] 横向项目:白莲崖水库工程碾压混凝土性能试验,2004; [10] 横向项目:流波水库工程碾压混凝土性能试验,2004; [11] 横向项目:大峡水电站混凝土配合比设计,2004; [12] 横向项目:江西省安福县柘田水库工程结构检测与安全评价,2004; [13] 横向项目:江西省泰和县缝岭水库工程结构检测与安全评价,2004; [14] 横向项目:江西省丰城县金桥水库混凝土与金属结构检测,2004; [15] 横向项目:江西省丰城县芦围水库混凝土与金属结构检测,2004; [16] 横向项目:红瓦屋面板混凝土试验研究,2005; [17] 横向项目:龙桥碾压混凝土配合比研究,2005; [18] 大型横向项目(合同金额 30 万元):构皮滩电站碱骨料试验研究,2005; [19] 大型横向项目(合同金额近 60 万元):惠州抽水蓄能水电站混凝土抗侵蚀耐久性研 究,2005; [20] 大型横向项目(合同金额 110 万元):磷矿渣粉在构皮滩电站中应用技术研究,2005。

大掺量矿物掺合料自密实混凝土抗碳化性能研究

大掺量矿物掺合料自密实混凝土抗碳化性能研究

大掺量矿物掺合料自密实混凝土抗碳化性能研究郑建岚;黄利频【摘要】设计了单掺粉煤灰和复掺粉煤灰与矿渣微粉的3个系列自密实混凝土试件.通过快速碳化试验、吸水试验,研究单掺粉煤灰和复掺粉煤灰与矿渣微粉对自密实混凝土抗碳化性能的影响.结果表明:当粉煤灰单掺掺量大于40%(质量分数)后,随着粉煤灰掺量的增大,自密实混凝土抗碳化能力迅速下降;粉煤灰与矿渣微粉复掺可显著缓和大掺量粉煤灰自密实混凝土抗碳化性能的下降.矿物掺合料对自密实混凝土抗碳化性能的影响存在正负效应.%One series of self-compacting concrete (SCO specimens incorporating fly ash and two series of SCC specimens incorporating both fly ash and ground granulated blast slag were designed. Based on accelerated carbonation and water absorption test, the effects of cement replacement by only fly ash and by both fly ash and slag powder on the carbonation resistance of SCC were studied. It is found that, when the replacement rate of fly ash is more than 40% (by mass), the carbonation depth of SCC increases rapidly as the replacement rate increases. However, replacement by both fly ash and slag powder greatly improves the carbonation resistance of SCC incorporating massive fly ash. Both positive and negative effects caused by mineral admixtures on carbonation resistance of SCC are analyzed.【期刊名称】《建筑材料学报》【年(卷),期】2012(015)005【总页数】6页(P678-683)【关键词】自密实混凝土;粉煤灰;矿渣微粉;碳化【作者】郑建岚;黄利频【作者单位】福州大学土木工程学院,福建福州350108;福州大学土木工程学院,福建福州350108【正文语种】中文【中图分类】TU528矿物掺合料对混凝土抗碳化性能有2个方面影响,一是矿物的微集料效应使混凝土内部孔隙细化,同时其活性效应使混凝土内部更加密实,减少了CO2的渗入,从而提高混凝土的抗碳化性能;二是矿物掺合料的二次水化反应减少了混凝土中Ca(OH)2含量,同时水泥用量的减少也使水泥水化产生的Ca(OH)2,C-S -H 凝胶等可碳化物质含量降低,从而导致混凝土抗碳化能力下降.自密实混凝土(SCC)具有良好的流动性、抗分层离析能力和穿越钢筋能力,近年来在实际工程中得到很好的应用[1].采用大掺量矿物掺合料是提高自密实混凝土各项性能的有效途径[2-3],因此大掺量矿物掺合料对自密实混凝土抗碳化性能的综合影响结果备受关注.目前有关自密实混凝土抗碳化性能的研究报道较少[4].本文旨在对比大掺量矿物掺合料自密实混凝土的碳化性能与普通混凝土(NC)的区别,探索大掺量矿物掺合料影响自密实混凝土碳化性能的规律,为自密实混凝土抗碳化性能的有关设计提供参考.1 试验1.1 原材料与配合比设计水泥:42.5普通硅酸盐水泥,其比表面积为348 m2/kg,密度为3.1g/cm3;粉煤灰:Ⅰ级粉煤灰,其比表面积为477m2/kg,密度为2.2g/cm3;矿渣微粉:S95矿渣微粉,其比表面积为471m2/kg,密度为2.94g/cm3;石子:花岗岩碎石,其粒径为5~20mm,表观密度为2 660kg/m3;砂:闽江河砂,其细度模数为2.32,表观密度为2 620kg/m3;外加剂:UNF-5萘系高效减水剂.水泥、粉煤灰和矿渣微粉的粒度分布采用激光粒度仪进行分析,结果见图1.水泥、粉煤灰和矿渣的化学组成见表1.图1 水泥、粉煤灰和矿渣微粉的粒度分布Fig.1 Particle size distribution of cement,fly ash and slag powder表1 水泥、粉煤灰和矿渣微粉的化学组成Tabel 1 Chemical compositions(by mass)of cement,fly ash and slag powder %Material SiO2 Fe2O3 Al2O3 CaO MgO SO3 Cl- Na2O K2O IL Cement 23.62 3.33 4.86 61.39 1.68 1.85 0.02 0.15 0.56 4.10 Fly ash 48.44 4.73 35.22 6.15 2.51 0.44 0.02 2.66 Slag powder 38.98 0.94 13.69 38.55 2.65 0.22 0.01 1.29设计了单掺粉煤灰、复掺粉煤灰与矿渣微粉自密实混凝土3个系列(SCCⅠ,SCCⅡ,SCCⅢ)试件,以及不掺矿物掺合料混凝土对比试件(NC-00).水泥和矿物掺合料总量为520kg/m3,水胶比1)文中涉及的水胶比、砂率等均为质量比或质量分数.为0.35,砂率为48%.SCCⅠ系列为单掺粉煤灰的自密实混凝土,粉煤灰取代水泥量(粉煤灰掺量)按20%,30%,40%,50%,60%,70%变化;SCCⅡ,SCCⅢ系列为复掺粉煤灰和矿渣微粉的自密实混凝土,粉煤灰和矿渣微粉复掺取代水泥量分别为30%和60%,粉煤灰与矿渣的比例按3︰7,1︰1,7︰3变化.混凝土配合比、工作性及28d抗压强度(σ28)见表2.新拌自密实混凝土坍落扩展度试验照片见图2.表2 混凝土配合比、工作性及28d抗压强度Table 2 Mix proportion,workability and 28dcompressive strength(σ28)of concreteNote:All theconcrete samples have the same water,sand and aggregate content,which are 182,786,852kg/m3,respectively.Mix proportion/(kg·m-3)Concrete Specimen code Replacement rate(r)/%Workabilit y σ28/Cement Fly ash Slag powder Superp MPa lasticizer Slump/mm Slumpflow/mm NC NC-00 0 520 0 0 6.24 260 550 52.2ⅠSCC-20 20 416 104 0 6.24 265 605 50.7 SCC-30 30 364 156 0 5.98 270 610 51.4 SCC-40 40 312 208 0 5.20 270 610 49.4 SCC-50 50 260 260 0 5.72 265 580 46.0 SCC-60 60 208 312 0 5.72 260 560 41.9 SCC-70 70 156 364 0 6.24 270 600 34.5 SCCⅡSCC-30-1 SCC-30-2 SCC-30-3 30 364 47 109 6.24 270 630 64.9 364 78 78 5.72 270 630 61.6 364 109 47 5.20 265 620 59.8ⅢSCC-60-1 SCC-60-2 SCC-60-3 60 208 94 218 6.24 270 635 64.3 208 156 156 5.72 280 670 61.1 208 218 94 5.20 275 670 53.8图2 新拌自密实混凝土坍落扩展度试验Fig.2 Slump flow test of fresh SCC1.2 试件的制作与养护测试混凝土碳化深度的试件为100mm×100mm×400mm棱柱体,每组2个试件,共13组;测试混凝土吸水率的试件为70.7mm×70.7mm×70.7mm立方体,每组2个试件,共13组.将成型好的试件用塑料薄膜覆盖表面,24h后拆模,然后放入标准养护室中养护.1.3 快速碳化试验将养护至26d龄期的碳化试件移入60℃的烘箱中放置48h,除留相对的两侧面外,其余表面用加热后的石蜡予以密封,然后按文献[5]方法进行快速碳化试验.当碳化至规定时间(7,14,28,42,56d)时,从碳化箱中取出试件,在压力机上劈裂切除试件一端,用石蜡将试件的切断面封好,再放回箱内继续碳化,直到下一测试期.将切除所得的试件部分刷去断面上残存的粉末,用1%酚酞酒精溶液测其碳化深度(XC).每个配合比测2个试件,取平均值.1.4 吸水试验试件标准养护至28d后,参照文献[6-7]的方法进行吸水试验.按式(1)计算出浸水时间24h内t(min)时混凝土试件单位面积的毛细孔吸水量Wt(kg·m-2),再由式(2)计算出混凝土试件毛细孔吸水系数w(kg·m-2·min-0.5).式中:m1为混凝土试件烘干涂蜡后的质量,g;mt为浸水t时混凝土试件的质量,g;A为混凝土试件的底面积,m2.w能较好地反映混凝土内部具有毛细吸水作用的毛细孔数量情况,并为较多的学者所采用[8-11].开口孔隙是指混凝土内部所有与外界相通的孔隙,包括了粗集料与水泥砂浆基体之间界面过渡区的孔隙.开口孔隙率PK(%)按式(3)计算.式中:m2为混凝土试件吸水恒重时的质量(g);V为混凝土试件的表观体积(m3);ρH2O为水的密度(取1 000kg·m-3).混凝土的w,PK越小,表明其孔径越细化、孔隙率越小,CO2越不易扩散至其内部.2 试验结果与分析2.1 快速碳化试验与吸水试验结果快速碳化试验与吸水试验结果见表3.表3 快速碳化试验与吸水试验结果Table 3 Results of accelerated carbonation and water absorption testConcrete Specimen code Carbonation depth(XC)/mm w/(kg·m-2·min-0.5) PK/%7d 14d 28d 42d 56d NC NC-00 0 0 0 0 0 0.091 6 9.63ⅠSCC-20 0 0 0 0 0 0 .072 0 7.69 SCC-30 1.25 1.53 1.89 2.17 2.35 0.070 0 7.57 SCC-40 1.33 1.74 2.18 2.76 3.27 0.053 0 6.54 SCC-50 3.82 4.58 5.54 6.47 7.42 0.057 9 7.40 SCC-60 5.36 6.89 8.21 9.54 10.82 0.058 9 7.58 SCC-70 9.36 11.65 15.34 17.89 19.72 0.071 6 9.06 SCCⅡSCC -30-1 0 0 0 0 0 0.054 0 6.24 SCC-30-2 0 0 0 0 0 0.057 3 6.94 SCC-30-3 0 0 0 0 0 0.061 6 6.54ⅢSCC-60-1 1.94 2.28 2.53 2.72 2.85 0.042 0 5.97 SCC-60-2 1.36 1.73 1.82 1.89 1.95 0.045 0 6.03 SCC-60-3 2.81 3.57 4.15 4.74 5.06 0.040 9 4.922.2 大掺量矿物掺合料对自密实混凝土碳化深度的影响2.2.1 单掺粉煤灰由表3可见,单掺粉煤灰的自密实混凝土(SCCⅠ系列),当粉煤灰掺量为20%时,其各龄期的碳化深度均为0,与普通混凝土一样显示了很好的抗碳化能力.当粉煤灰掺量≥30%,随着粉煤灰掺量的增大,同龄期自密实混凝土碳化深度逐步增大,但粉煤灰掺量在40%以内时自密实混凝土碳化深度依旧较小,当粉煤灰掺量超过40%后,自密实混凝土碳化深度迅速增大,例如粉煤灰掺量为50%,60%,70%的自密实混凝土(SCC-50,SCC-60,SCC-70),其28d碳化深度分别是同龄期粉煤灰掺量为40%自密实混凝土(SCC-40)的2.54,3.77,7.04倍. 图3给出了碳化28d时单掺粉煤灰自密实混凝土碳化深度(XC,28d)与粉煤灰掺量(rF≥30%)关系的拟合曲线.单掺粉煤灰自密实混凝土碳化深度与粉煤灰掺量关系的二次函数表达式如式(4)所示.图3 28d单掺粉煤灰自密实混凝土碳化深度与粉煤灰掺量关系的拟合曲线Fig.3 Fitting curve of relationship between 28dcarbonation depth of SCC Ⅰand replacement rate(rF)of fly ash2.2.2 复掺粉煤灰与矿渣微粉由表3可以看出:(1)就粉煤灰与矿渣微粉复掺取代水泥量同为30%的SCCⅡ系列而言,所有复掺粉煤灰与矿渣微粉自密实混凝土试件的各龄期碳化深度均为0,与单掺20%粉煤灰自密实混凝土的情况一样,表现出很好的抗碳化性能.(2)就粉煤灰与矿渣微粉复掺取代水泥量同为60%的SCCⅢ系列而言,所有不同复掺比例的自密实混凝土(SCC-60-1,SCC-60-2,SCC-60-3)各龄期碳化深度均较单掺60%粉煤灰自密实混凝土(SCC-60)明显降低,例如SCC-60-1,SCC60-2,SCC60-3的28d碳化深度分别只有SCC-60的30.8%,22.2%,50.5%.当粉煤灰与矿渣微粉复掺比例为1︰1时,自密实混凝土(SCC-60-2)抗碳化能力最好,其在28,42,56d的碳化深度均小于单掺30%粉煤灰自密实混凝土(SCC-30).因此,使用粉煤灰与矿渣微粉的复掺技术,可显著缓和单掺粉煤灰自密实混凝土抗碳化能力的下降,从而使大掺量粉煤灰自密实混凝土的抗碳化性能得到保证.2.3 大掺量粉煤灰自密实混凝土可碳化物质含量根据水泥及粉煤灰中各组分氧化物的质量分数(见表1),运用Bogue's公式可先计算出各熟料矿物C3S,C2S,C3A,C4AF在水泥中所占的质量分数;根据熟料矿物参与的水化反应、粉煤灰中活性SiO2,Al2O3参与的火山灰反应,以及水泥、粉煤灰在混凝土中所占的质量分数(见表2),由文献[12]公式可计算得出混凝土试件在养护28d时可碳化物质Ca(OH)2及C-S-H凝胶的含量,见表4.计算中,假设C-S-H凝胶组成为3CaO·2SiO2·3H2O,养护28 d时C3S,C2S,C4AF的水化反应程度分别为90%,75%,55%;粉煤灰中具有火山灰反应活性的SiO2,Al2O3占其氧化物质量分数均为85%,粉煤灰火山灰反应程度为10%.由表4可以看出,随着粉煤灰掺量的增大,混凝土中可碳化物质含量下降,其抗碳化能力随之下降.表4 混凝土中可碳化物质含量Table 4 Carbonable substance content in concreteCarbonable substance Content/(mol·m-3)70 Ca(OH)21261 810 585 360 134 147 31 C-S-H g NC-00SCC-20SCC-30SCC-40SCC-50SCC-60SCC-el 814 687 623 560 496 390 3072.4 毛细孔吸水系数(w)及开口孔隙率(PK)从表3可以看出:(1)掺入粉煤灰后,所有自密实混凝土的毛细孔吸水系数(w)和开口孔隙率(PK)均小于不掺粉煤灰的普通混凝土(NC-00).(2)就单掺粉煤灰自密实混凝土(SCCⅠ系列)而言,随着粉煤灰掺量的增大,w和PK均呈现先降后升的变化趋势,当粉煤灰掺量为40%时,w与PK均达到最小值,分别为NC-00的57.9%,67.9%.吸水试验结果表明,对于单掺≤60%粉煤灰的自密实混凝土,混凝土内部开口孔隙率下降,粉煤灰的填充作用使有害毛细孔数量下降,材料大孔减少,且粉煤灰掺量为40%时混凝土最为密实,有害毛细孔数量相比最低.笔者对比水泥用量在500~550 kg/m3、水胶比在0.32~0.37之间的掺粉煤灰普通混凝土碳化试验结果[13-16]发现,相同粉煤灰掺量条件下,自密实混凝土的碳化深度明显较小.这是由于自密实混凝土采用质量高的粉煤灰,自密实混凝土对骨料级配要求较高;在大掺量粉煤灰条件下,自密实混凝土避免了普通混凝土在振捣下易出现的浮灰现象,因而匀质性较好,结构更加致密,抗碳化性能更好.复掺粉煤灰与矿渣微粉的自密实混凝土(SCCⅡ,SCCⅢ系列),其毛细孔吸水系数(w)和开口孔隙率(PK)与单掺粉煤灰自密实混凝土(SCCⅠ系列)相比又有一定程度的下降(见表3).在取代水泥量同为30%的情况下,SCCⅡ系列中SCC-30-1,SCC-30-2,SCC-30-3的 w 分别只有SCCⅠ系列中SCC-30的77.1%,81.9%,88.0%;在取代水泥量同为60%的情况下,SCCⅢ系列中SCC-60-1,SCC-60-2,SCC-60-3的 w 分别只有SCCⅠ系列中SCC-60的71.3%,76.4%,69.4%.2.5 综合分析综上分析,可以看出,矿物掺合料一方面使自密实混凝土内部更加致密,减少了CO2的渗入,从而提高自密实混凝土的抗碳化性能.另一方面水泥用量减少及二次水化反应使自密实混凝土中Ca(OH)2及C-S-H凝胶等可碳化物质含量降低,从而导致自密实混凝土抗碳化能力下降.自密实混凝土抗碳化能力的大小是上述正负效应共同作用的结果.从混凝土密实性角度来看,单掺粉煤灰掺量在40%以内时,随着粉煤灰掺量的增大,CO2更难进入自密实混凝土内部,自密实混凝土抗碳化性能越好,但从自密实混凝土碳化深度测试结果来看,尽管粉煤灰掺量在40%时自密实混凝土碳化深度仍较小,但粉煤灰掺量≥30%后自密实混凝土碳化深度随着粉煤灰掺量的增大而增大.也就是说,当粉煤灰掺量≥30%后,虽然自密实混凝土的密实性仍然能够继续得到改善,但水泥用量的减少及粉煤灰活性效应导致的混凝土可碳化物质含量的下降对自密实混凝土抗碳化性能起了主导作用,因此随着粉煤灰掺量的增大,自密实混凝土抗碳化性能下降.对于粉煤灰与矿渣微粉复掺的自密实混凝土,吸水试验结果说明,在相同取代水泥量条件下,与单掺粉煤灰相比,其w与PK值明显下降.这说明粉煤灰和矿渣微粉复掺后,不同粒径分布的粉煤灰、矿渣微粉、水泥相互填充,使自密实混凝土孔径更加细化、孔隙率减小,CO2扩散至自密实混凝土内部的阻力增大.粉煤灰与矿渣微粉复掺取代水泥量为60%时,混凝土最为密实,当粉煤灰与矿渣微粉复掺比例为3︰7,1︰1时,自密实混凝土碳化深度接近甚至小于单掺30%粉煤灰的混凝土,如SCC-60-2在28d之后的碳化深度均小于SCC-30.因此,粉煤灰与矿渣微粉复掺使大掺量粉煤灰自密实混凝土密实度进一步提高,明显缓和了可碳化物质含量下降对其抗碳化性能的不利影响.3 结论(1)单掺20%粉煤灰时,自密实混凝土与普通混凝土一样,各龄期碳化深度为0;单掺30%~40%粉煤灰时,自密实混凝土碳化深度仍然较小;当单掺粉煤灰掺量大于40%后,随着粉煤灰掺量的增大,自密实混凝土抗碳化能力迅速下降.(2)粉煤灰与矿渣微粉复掺可明显缓和大掺量粉煤灰自密实混凝土抗碳化性能的下降.当粉煤灰与矿渣微粉复掺取代水泥量为30%时,自密实混凝土与单掺20%粉煤灰自密实混凝土一样,各龄期碳化深度均为0;当粉煤灰与矿渣微粉复掺取代水泥量为60%时,按1︰1复掺粉煤灰与矿渣微粉时效果相比最好,自密实混凝土28d后的碳化深度小于单掺30%粉煤灰自密实混凝土.(3)矿物掺合料对自密实混凝土抗碳化性能的影响存在正负效应.当单掺粉煤灰掺量≥30%时,因大掺量粉煤灰使自密实混凝土可碳化物质含量的下降对混凝土抗碳化性能产生的不利影响,大于粉煤灰改善自密实混凝土密实性对抗碳化性能产生的有利作用.复掺粉煤灰与矿渣微粉使混凝土密实度进一步提高,显著改善了自密实混凝土可碳化物质含量下降对其抗碳化性能产生的不利影响.参考文献:[1]罗素蓉,郑建岚.自密实混凝土在加固工程中的应用研究[J].建筑材料学报,2006,9(3):330-336.LUO Su-rong,ZHENG Jian-lan.Study on the application of self-compacting concrete in strengthening engineering [J].Journal of Building Materials,2006,9(3):330-336.(in Chinese)[2]薛明,刘晓旭,曹黎明.复合矿物掺料对自密实混凝土耐盐腐蚀性能影响的研究[J].粉煤灰,2008(2):23-25.XUE Ming,LIU Xiao-xu,CAO Li-ming.Study on effect of compound mineral mixture on anti-salt corrosion of self-compacted concrete[J].Coal Ash,2008(2):23-25.(in Chinese)[3]周虎,安雪晖,金峰.低水泥用量自密实混凝土配合比设计试验研究[J].混凝土,2005(1):20-23.ZHOU Hu,AN Xue-hui,JIN 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Chinese)[14]金祖权,孙伟,张云升,等.粉煤灰混凝土的多因素寿命预测模型[J].东南大学学报:自然科学版,2005,35(S):149-154.JIN Zu-quan,SUN Wei,ZHANG Yun-sheng,et al.Multi-factor service life prediction model for concrete with fly ash[J].Journal of Southeast University:Natural Science,2005,35(S):149-154.(in Chinese)[15]金祖权,孙伟,张云升,等.荷载作用下混凝土的碳化深度[J].建筑材料学报,2005,8(2):179-183.JIN Zu-quan,SUN Wei,ZHANG Yun-sheng,et al.Study on carbonation of concrete under loading[J].Journal of Building Materials,2005,8(2):179-183.(in Chinese)[16]刘志勇,孙伟.与钢筋脱钝化临界孔溶液pH值相关联的混凝土碳化理论模型[J].硅酸盐学报,2007,35(7):899-903.LIU Zhi-yong,SUN Wei.Theoretical carbonation model related with pore solution pH value for steel bar depassivation in concrete[J].Journal of the Chinese Ceramic Society,2007,35(7):899-903.(in Chinese)。

过度开采矿资源的英语作文

过度开采矿资源的英语作文

日本明治时代报业的发展研究日本明治时代(1868年-1912年)是日本历史上一个重要的时期,这个时期发生了许多重大的变革与进步。

在这个时期,日本报业也经历了巨大的发展和变革。

明治时代初期,日本的报业还处于起步阶段。

1869年,日本政府颁布了《新聞記事律》,该法规定了日本的报纸出版行为。

根据这个法律,只有经过政府的审核和批准的报纸才能够出版。

起初日本的报业主要是政府官方的报纸,比如《政府公报》。

这些报纸主要是为了宣传政府的政策和宣传。

随着时代的变迁和社会的发展,日本的报业逐渐朝着自主独立的方向发展。

1881年,《东京邮报》成立,这是日本第一家私人报纸。

《东京邮报》的创立标志着日本报业的起步,也开创了日本私人报业的先河。

随着时间的推移,越来越多的私人报纸出现,形成了日本的报业市场。

在明治时代末期,日本的报业经历了快速发展。

新闻报道的内容也开始多样化。

除了政治新闻,更多的关注社会新闻、文化新闻等。

日本的报业也发展出了不同的类型。

除了日报和周报,还出现了专业性的报纸,比如专门报道经济和商业新闻的报纸、专门报道体育新闻的报纸等。

这个时期的日本报业之所以能够取得如此巨大的发展,离不开一些重要的因素。

社会经济的发展为报业提供了丰富的资本和市场。

明治时代是日本现代工业化的起点,经济腾飞为报业的发展提供了良好的经济基础。

报纸在明治时代被广泛运用于宣播政府政策和教育国民的工具,政府对报业的支持和引导也起到了重要的作用。

报业出版技术的发展也为报纸的发行和传播提供了便利。

印刷技术的进步使得报纸的印刷速度和质量都得到了大幅提升,报纸的阅读范围也得到了扩大。

日本明治时代的报业发展经过了从政府主导到私人独立的发展过程。

在这个时期,日本的报业从最初的政府官方报纸发展到了私人报纸,不仅内容更加多样化,类型也更加丰富。

报纸成为了宣传政策、传递信息的重要工具,对于当时日本社会的变革和进步起到了积极的推动作用。

日本报业的发展离不开社会经济的发展、政府的支持和技术的进步等多方面因素的综合作用。

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The influence of mineral admixtures on the rheology of cementpaste and concreteChiara F.Ferraris a,*,Karthik H.Obla b,Russell Hill ba NIST,100Bureau Drive,Mail Stop8621,Gaithersburg,MD20899,USAb Boral Material Technologies,45N.E.Loop410,Suite700,San Antonio,TX78216,USAReceived3March2000;accepted12October2000AbstractRheological tests on cement paste were used to successfully select the type and dosage of mineral admixtures that improved concrete workability.Among the six different mineral admixtures tested,the ultrafine fly ash(UFFA)was determined to give the best results by reducing the yield stress and viscosity.These improved rheological properties were not achieved by increasing the water demand and/or the high-range water reducer(HRWR)admixtures dosage.Therefore,the addition of UFFA improved the concrete flow without a potential decrease of the hardened properties or an increase in cost.The conclusions reached based on cement paste tests were validated by concrete slump tests.The cement paste rheological data were also compared using two simpler tests,minislump and Marsh cone.The goal was to determine whether the simpler tests could be used to characterize the rheology of cement paste adequately.The conclusions are that these simpler tests are unreliable for measuring workability.D2001Elsevier Science Ltd.All rights reserved.Keywords:Rheology;Cement paste;Workability;Fresh concrete1.IntroductionHigh-performance concrete(HPC)is a complex mixture often containing5±10different materials.Interaction between the various materials can cause wide variations in workability,which also depends on the specific materials and proportions used.Determining workability properties by testing concrete is not always practical.Extensive con-crete testing requires a large amount of materials and labor, which is expensive.There is,therefore,a need to predict the workability of concrete through a simpler,cheaper labora-tory approach.This paper describes an attempt to utilize rheological measurements in cement paste as a reasonable indicator of concrete workability.Concrete workability is defined,according to American Concrete Institute(ACI),as the ease of placement of concrete and is usually quantified by the result of the slump cone test.Rheological tests on cement paste were used to select the type and dosage of mineral admixtures that improved concrete workability.The conclusions reached based on cement paste tests were validated by concrete slump tests. It was also deemed interesting to compare the fundamental parameters(yield stress and viscosity)measured with a fluid rheometer with the results from two commonly used empiri-cal tests,the minislump and the Marsh cone tests.If a relationship could be established,the empirical tests could be used to design materials for a given yield stress and viscosity or,at the very least,rank different materials base on yield stress or viscosity.The decision to study the influence of mineral admixtures was dictated by the recent increase in use of mineral admixtures for improved concrete durability.Economics (lower cement requirement)and environmental considera-tions have also had a role in the growth of mineral admixture usage.The lower cement requirement also leads to a reduction in the amount of carbon dioxide generated by the production of cement,while the use of a mineral admixture utilizes a product that would ordinarily be bound for the land fill.Thus,there is a double environmental benefit from using mineral admixtures.*Corresponding author.Tel.:+1-301-975-6711;fax:+1-301-990-6891.E-mail address:clarissa@(C.F.Ferraris).Cement and Concrete Research31(2001)245±2550008-8846/01/$±see front matter D2001Elsevier Science Ltd.All rights reserved.PII:S0008-8846(00)00454-32.Background2.1.Concrete workability characterizationConcrete workability cannot necessarily be sacrificed for improved hardened properties,such as durability or strength.Workability is typically quantified in the field by the result of the slump cone test.Nevertheless,a survey[1] conducted by the National Ready-Mixed Concrete Association(NRMCA)and the National Institute of Standards and Technology(NIST)determined that,for HPC,the slump cone value is not representative of the ease of handling HPC in the field.It was reported that concrete mixtures with the same slump might not behave the same way during placement.This implies that the slump value does not give enough data to fully characte-rize concrete flow.In the construction field,terms like workability,flow-ability,and cohesion are used,sometimes interchangeably, to describe the behavior of concrete under flow.The definitions of these terms are very subjective.Therefore, there is a need for a more fundamental and quantitative description of concrete flow.Rheological measurements of concentrated suspensions can be used to describe the flow of concrete.Numerous researchers[2±4]have successfully used the Bingham equation.Two parameters define the flow:yield stress and plastic viscosity[5].Yield stress is related to slump[6,7],but plastic viscosity is usually ignored because only a few type of instruments exist to measure it[8].However,the viscosity may be related to properties such as stickiness,placeability,pumpability,and finishability.In addition,segregation could be defined as the ability of the aggregate to migrate(or sink)in the cement paste.This phenomenon is linked to the viscosity of the cement paste and the concrete mixture design.Therefore, methods to predict concrete workability need to take into account more than just the yield stress.2.2.Concrete rheology from cement paste rheologyAdmixtures mainly affect the flow behavior of the cement paste without altering the composition or behavior of the aggregates.Therefore,it seems reasonable to try to select admixtures,chemical and mineral,by only testing the cement paste.Ideally,the results will then be related to the concrete workability.Unfortunately,the relationship between cement paste rheology and concrete rheology has never been completely established.The main reason for this is that cement paste rheology is typically measured under conditions that are never experienced by the cement paste in concrete.Therefore,the measured cement paste rheological parameters may differ from those estimated from concrete parameters.The values usually reported in the literature for cement paste do not take into account the contribution of the aggregates[9].The aggregates act as heat sinks and shear the cement paste during the mixing process.A computerized model to simulate the concrete being sheared is under development at NIST[10].This model will predict concrete rheology from constituent properties that will include rheological measurements on cement paste.However,the cement paste flow properties,if measured ``properly,''can be used to screen mineral admixtures.The details of the methodology are presented elsewhere[11], but the following principles should be reiterated.The cement paste needs to be mixed and tested under the conditions similar to those that it will experience in concrete,primarily shear and temperature history.There-fore,a high-shear,temperature-controlled mixer should be used.To measure the rheological parameters of cement paste flow,a parallel plate rheometer must be used because it is the only rheometer with variable geometry.It has been established[12]that the rheological properties of cement paste change if the material is squeezed between two surfaces or aggregates as in concrete.The distance between the surfaces is called the``gap.''In a parallel plate fluid rheometer,the gap or distance between the plates can be varied easily to more closely represent the shearing action imposed on paste in concrete.In this paper,cement paste rheological parameters were measured using the above method as a function of type and dosage of mineral admixture.2.3.Role of fine powder additions on workabilityIt is usually reported that,if the volume concentration of a solid is held constant,the addition of mineral admixtures improves concrete performance but reduces workability.The most common reason for poor work-ability is that the addition of a fine powder will increase the water demand due to the increase in surface area.This belief is supported by test results that show that the addition of fine silica fume(SF)particles increases the water demand to attain specific workability levels.How-ever,in certain cases,it is reported in the literature that the use of fine mineral admixtures can reduce the water demand or increase the nge et al.[13]measured the water demand of mortars with increasing additions of a very fine blast furnace slag.He found that,for a specific flow,an optimum amount of blast furnace slag reduced the water demand of the mortar.A popular hypothesis put forward to explain the workability enhancement due to the use of certain fine mineral admixtures,especially fly ash (FA)or SF,is that the spherical particles easily roll over one another,reducing interparticle friction[14].The sphe-rical shape also minimizes the particle's surface to volume ratio,resulting in low fluid demands.Out of all3D shapes, a sphere gives the minimum surface area for a given volume[15].Sakai et al.[16]reported that a higher packing density was obtained with spherical particles as compared to crushed particles in a wet state.This resulted in lower water retention in the spherical case and subse-C.F.Ferraris et al./Cement and Concrete Research31(2001)245±255 246quently lower water demand for a specific workability.A strong dependence of fluidity(defined as the inverse value of the viscosity)on the average particle size was reported with a pessimum value[16].It was explained that,at an optimal particle size,the packing density was maximum, which helped to achieve maximum fluidity.Recently, Collins and Sanjayan[17]reported that in concrete con-taining alkali-activated ground granulated slag as the binder,the workability was improved by replacing partof the binder with ultrafine materials.This material had 90%by mass of the particles smaller than13.7m m.It was also reported that some similar materials were not effective in improving the workability.It can be concluded from this survey of the literature that the selection of a fine mineral admixture for improved concrete workability is not a trivial problem.At present,this selection cannot be predicted from the physical or chemical characteristics of the admixture,and can only be determined using a properly designed test.3.Materials,mixing,and testing detailsThe materials,mixing,and testing requirements provided here are for the cement paste tests only.The details for the concrete test program are provided in Section5.3.1.MaterialsThe cement was an ASTM Type I portland cement whose composition is described in Table1.This cement was used for all tests,both concrete and cement paste.The high-range water reducer(HRWR)was a naphthalene sulfonate-based product with a mass fraction of43%active ingredients.The mineral admixtures used are shown on Table2with their mean particle diameters(PDs).The mean PD was measured using a laser diffraction particle size analyzer.Four different FAs,all from the same plant, were tested.FA was the standard FA available in that plant and used in concrete type applications.Coarse fly ash (CFA)was a coarse ash that is usually rejected as it does not meet the ASTM C618requirements for particle size. Fine fly ash(FFA)is a finer form of ash obtained by separation from a coarser ash using a classifier.Ultrafine fly ash(UFFA)is an ultrafine ash obtained by still more rigorous separation.The cement paste composition was varied to explore the influence of mineral admixture dosage and type on the rheological properties.The performance differences in the paste due to the addition of mineral admixture were mea-sured either by the rheological properties at constant water content or by the water reduction at constant mineral and chemical admixture dosage.The compositions of the cement pastes can be summarized as follows:water/cement ratio:0.28±0.35;dosages of mineral admixtures:0±16%of cement,replacing cement by mass;anddosage of HRWR(based on naphthalene sulfonatedcondensate):0.45±0.70%solid by mass of cementi-tious materials.3.2.Cement paste preparationThe cement paste preparation is very important because the shear history of a mixture will influence its rheological behavior.In this case,we wanted to have the same shear history as in the concrete in order to be able to compare the neat cement paste behavior and the concrete flow.Two types of mixers were considered:a standard paddle mixer[18]and a high-speed blender.The cement paste was mixed using a paddle mixer according to the procedure of ASTM C305, except that no sand was added.The second mixer used was a large(4L)blender.This blender was not temperature controlled.The cement paste mixture was prepared according to the following procedure.The cement and the mineral admixture(if any)weremixed dry for about5s by hand outside the mixer. Water was poured into the4-L blender.The mixer was started at slow speed and the cement±mineral admixture mixture was added over a50-speriod.The HRWR was added in5s.The mixture was mixed for another60s at slow speed.Table1Cement compositionChemical composition Percentage by mass Loss on ignition(LOI) 1.29Sulfur trioxide(SO3) 2.79Silica dioxide(SiO2)20.86Ferric oxide(Fe2O3) 3.47 Magnesium oxide(MgO) 1.21 Aluminum oxide(Al2O3) 4.60 Equivalent alkalies(as Na2O)0.46Calcium oxide(CaO)64.34Free lime±Insoluble residue(IR)0.1 Tricalcium silicate(C3S)59.57 Tricalcium aluminate(C3A) 6.31Table2Mineral admixtures Mean PD[m m] 1Coarse Fly Ash(CFA)18.02Fly Ash(FA)10.96Fine Fly Ash(FFA) 5.73Ultra Fine Fly Ash(UFFA) 3.14Metakaolin(MK)7.45Silica Fume(SF)%0.1C.F.Ferraris et al./Cement and Concrete Research31(2001)245±2552473.3.Cement paste testing detailsFresh cement paste specimens were tested first in a parallel plate fluid rheometer and then using the minislump and Marsh cone.The testing details are given below.3.3.1.Parallel plate rheometerThe parallel plate rheometer was used to determine the yield stress and the plastic viscosity as defined by Bingham.The distance between the two plates of the parallel plate rheometer should be selected based on the cement paste content in the concrete mixture to be characterized.How-ever,as this method was used here as a screening test,and no comparison was sought with a specific concrete mixture design,the gap (distance between the plates)was arbitrarily fixed at 0.4mm,based on the median value of distance between aggregates in concrete [11].The shear rate used ranged from 3to 50s À1.This range was selected to correspond to the shear rates used in a concrete rheometer [7].The surfaces of the two plates were serrated,as provided by the manufacturer,to avoid slippage.The following is a list of the sequence of the measurements done..One milliliter of cement paste was placed,using a syringe,on the bottom plate..The two plates were brought together to the desired distance of 0.4mm..The computer driven system imposed a slowly increas-ing shear rate from 0to 70s À1in 160s.As soon as the highest shear rate was reached,the plate stopped rotating..After this first phase (needed to homogenize the specimen),a full cycle of increasing shear rate by 10steps from 3to 50s À1and back to 0shear rate with another 10steps was performed.At each step,the stress was measured and the value of constant stress was recorded.If the constant stress was not achieved in 20s,the computer took the average of the last five values recorded..The slope of the down-curve (decreasing shear rate)was used to calculate the plastic viscosity,while the inter-cept at zero shear rate was used to calculate the yield stress.An example of the curve obtained is shown in Fig.1.3.3.2.Minislump cone test detailsKantro [19]developed the minislump cone test.The test was conducted as follows:A square piece of flat glass on which the diagonals and the median were traced was covered with a plastic sheet.The plastic sheet is needed to avoid water or very fluid paste leakage under the minicone.The minislump cone was placed in the center of the glass plate and filled with the cement paste.The cone was gently lifted and after one minute the diameter of the pad formed was measured along the marked line on the glass in four directions.All four diameters were recorded and the average diameter was calculated.3.3.3.Marsh cone test detailsThe Marsh cone is a funnel with a long neck and an opening of 5mm,currently used to test oil well cement [20].This test is not a standard test.The test was conducted using the following procedure..A Marsh cone was attached to a stand so that the small orifice was pointing down and a glass graduated cylinder was placed under the cone..Closing the small orifice with a finger,1L of cement paste was poured into the cone..The orifice was opened and a stop watch started..The time for a certain amount of cement paste to flow was recorded.The volumes selected were 300,500,and 700mL.These settings were selected from research conducted by Nehdi et al.[21]that showed a nonlinear flow of the cement paste for amounts higher than 700mL.4.Results and discussion4.1.Effect of mixer type on rheological properties of cement pasteThe goal of testing cement paste instead of concrete is to save materials and labor.However,to be useful,the cement paste results need to predict concrete performance.There-fore,the cement paste needs to be sheared with about the same intensity,as it would have experienced while being mixed in concrete.One way to determine if the mixing method selected is appropriate is to select several cement paste compositions and compare the rheological behavior of the cement paste with the concrete performance.In this paper,we selected cement paste with and without mineral admixtures.The key result,which would tell us that we had the correct mixing method,is that the mineral admixture that resulted in the larger reduction in yield stress or viscosity compared to the control,which had no mineral admixture,would be the same in cement paste and in concrete.The two mixers available to us were a Hobart and ablender.Fig.1.Typical curve obtained from the fluid rheometer.C.F .Ferraris et al./Cement and Concrete Research 31(2001)245±255248To perform the comparison,we selected three mineral admixtures(metakaolin(MK),UFFA,and SF)to test in cement pastes.If the selection of the best mineral admixture was based on the data shown in Fig.2,the result would depend on the mixer used.Consider the yield stress(YS) behavior(bars and left axis).The best admixture should reduce the yield stress compared to the control(no admix-tures).If the black bars(paddle mixer)are examined,the best admixture will be the MK,while if the gray bars are examined,the choice will be UFFA.In examining the results obtained with concrete[23],for equivalent slumps, the water demand is the lowest for mixtures containing UFFA.In other words,UFFA increases slump in concrete when water content is kept constant.In conclusion,UFFA is the``best''admixture both in concrete and in cement paste if mixed in a blender.Therefore,concrete performance was more accurately predicted by the cement paste mixed in the blender and not in the Hobart mixer.This confirms a studyby Helmuth et al.[22]stating that in concrete,during mixing,the cement paste is sheared with an energy and rate more closely reproduced in a blender as opposed to the low shear rate of the Hobart mixer.Therefore,to predict concrete behavior,it is essential to use the correct mixer while preparing cement paste.Thus,the rest of the data reported in this paper were obtained using the blender.parisons between rheological and empirical testsA fluid rheometer for cement paste is not widely avail-able in the construction industry for many reasons.The two main reasons are:(1)the instrument is relatively expensive (on the order of US$40,000)and(2)the importance of using such a device for cement paste was not advocated until recently[11,12].Therefore,it would be advantageous to be able to use simpler tests such as the minislump and the Marsh cone tests.A comparison between the rheometer and the other test results is presented in Figs.3and4.These figures are a compilation of all the tests conducted in this research program using a blender to mix the cement paste. Each point represents various mineral admixture additions at various dosages,W/C,and HRWR dosages.The plot of yield stress vs.minislump spread diameter (Fig.3)shows a weak correlation:Higher yield stress corresponds to a lower spread in the minislump.There-fore,an indication of the yield stress could be obtained using the minislump.This result was expected because the cement paste in a minislump test will only flow if the stress due to the weight of the cement paste contained in the cone is high enough,i.e.,higher than the yield stress of the cement paste.It should be kept in mind that the minimum diameter that can be measured is70mm, corresponding to the diameter of the bottom of the cone. Therefore,despite some of the scatter of the data shown on Fig.3,an approximation of the yield stress could be obtained by fitting a straight line through the data.This parison between the minislump spread and yield stress.Each point represents a measurement(not an average),therefore,no estimate of the uncertainty can becalculated.Fig.2.Influence of the mixer on the rheological properties of cement paste.``YS''is the yield stress and``Visc.''is the plasticviscosity.parison between the marsh flow time and plastic viscosity.Eachpoint represents a measurement(not an average),therefore,no estimate ofthe uncertainty can be calculated.C.F.Ferraris et al./Cement and Concrete Research31(2001)245±255249fit will not be done here because it has a limited significance due to the wide scatter of the data.In contrast,the plot of time to flow for300ml(Marsh cone flow test result)and the viscosity(Fig.4)shows no correlation at all.If outliers are removed,a``shot gun'' distribution can be observed.Similar results were obtained when the times to flow for500or700ml were plotted, because the time to flow had a linear relationship with the amount of material measured.Nevertheless,in some limited cases,a lower time to flow does correspond to a lower viscosity.However,it would be dangerous to rely on the Marsh cone to select a material for a certain viscosity requirement or even to rank materials based on viscosity due to the overall lack of correlation.This result is some-what unexpected because it was assumed that the weight of the cement paste was high enough to overcome the yield stress and therefore the speed of the cement paste flow through the flow cone would depend on its viscosity.From the results obtained,it seems that other factors contribute to the flow,such as friction and sedimentation.4.3.Effect of mineral admixture type on cement paste rheological propertiesIn Fig.5,the yield stress and viscosity are shown for mixtures composed of cement paste with the same W/C ratio of0.35and varying dosages of HRWR.The amounts of the various mineral admixtures by mass as replacement of cement are indicated on the figure.It is clear that the replacement of cement with UFFA leads to a decrease in the HRWR dosage over the control(no mineral admixtures)at a given yield stress or viscosity.In contrast,the replacement of cement by SF significantly increases the HRWR dosage at a given yield stress and viscosity.The addition of MK shows no significant improvement in yield stress and plastic viscosity over the control.Therefore,there are no significant rheological benefits or drawbacks in using MK as a mineral admix-ture,at least at the dosages tested.4.4.Effect of PD on cement paste rheological properties In Fig.6,the rheological measurements for the four FA/cement pastes are plotted against the mean particle size of the FAs.All tests were conducted at the same dosage of mineral admixture(12%replacement of cement by mass),same W/C ratio(0.35)and same dosage of HRWR(0.45%solid by mass of cement).It is clear that the lowest yield stress and viscosity are obtained at a mean PD of3m m.This value corresponds again to UFFA.It also seems that maximum viscosity is reached at a mean PD of about11m m,and maximum yield stress at a mean PD of5.7m m.This result seems to indicate an optimum and a pessimum PD,with the optimum at3m m and the pessimum at5.7m m.Unfortunately,a FA with a smaller PD than3m m was not available to determine if the correct optimum was reached.Sakai et al.[16]also showed that there is a pessimum at18m m,but he used limestone powder and not FA.It is conceivable that the optimum and pessimum value depends on the type of mineral admixture used,and the chemistry and physics of the individual particles.4.5.Effect of W/C on rheological properties of cement paste Fig.7shows the results of tests performed on cement pastes with UFFA(at12%replacement)at various W/C ratios,plotted vs.HRWR dosage.There are several ways to use or to interpret these results:(1)determine the correct dosage of HRWR needed to obtain the same yield stress and/or viscosity with the UFFA mixes and the control at various W/C;(2)determine the water reduction achieved by using UFFA and maintaining the same yield stress and/or viscosity;or(3)determine the reduction inHRWRFig.5.Dosage of HRWR and its effect effect on the flow of properties.The W/C ratio was0.35.The error bars represent an estimate percentage error:1.7%on yield stress and10%viscosity.This error was estimated from the numerous tests done.C.F.Ferraris et al./Cement and Concrete Research31(2001)245±255250dosage achieved while maintaining the same yield stress and/or viscosity.In summary,the addition of UFFA improves the rheolo-gical properties.If the goal is to add UFFA and achieve the same yield stress and viscosity as the control,Fig.7shows that the W/C ratio can be reduced by 10%and the HRWR dosage can be reduced by 40%.On the other hand,if the water content is reduced by 20%(W/C ratio of 0.28)a significant increase of the HRWR dosage (almost double)is needed to maintain the yield stress or viscosity,giving the same rheological behavior as the SF mixes.4.6.Effect of dosage of UFF A on cement paste rheological propertiesFig.8shows the influence of dosage of UFFA on cement paste rheological properties.The tests were done at a W/C ratio of 0.35and a fixed HRWR dosage of 0.45%solid by mass of cement.The plot suggests that a dosage of 12%bymass is optimal for the best rheological properties.The dosage shows an optimum value corresponding to the lowest value achieved by the yield stress for a 12%UFFA by mass dosage.The shape of the curve (Fig.8)is an important result because it corresponds to the same type of behavior seen in concrete,as will be shown in Section 6and in Fig.10.5.Concrete testing 5.1.Concrete mixtureThe purpose of the concrete measurements was to validate the conclusions drawn from the data obtained in the cement paste for the best type and dosage of mineral admixture.The concrete rheological behavior was tested using the standard slump cone test.Therefore,only an indication of the yield stress was available forcomparison.Fig.6.Influence of mean PD on the flow properties of cement paste.The W/C ratio was 0.35.The error bars represent an estimate percentage error:17%on yield stress and 10%viscosity.This error was estimated from the numerous testsdone.Fig.7.Influence of W/C ratio on the rheological properties of cement paste with UFFA at 12%replacement of cement by mass.The numbers in the legend indicate the W/C ratio used.The error bars represent an estimate percentage error:17%on yield stress and 10%viscosity.This error was estimated from the numerous testsdone.Fig.8.Influence of the dosage of UFFA on the rheological properties of cement paste with constant dosage of HRWRA (0.44%(13oz/100lb of cementitious materials)).The W/C ratio was 0.35.The error bars represent an estimate percentage error:17%on yield stress and 10%viscosity.This error was estimated from the numerous tests done.C.F .Ferraris et al./Cement and Concrete Research 31(2001)245±255251。

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